#Calgary water filter systems

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Humidifier Installation: Enhancing Comfort in Your Home

As winter settles in, maintaining optimal humidity levels in your home is essential for comfort and health. A humidifier can help alleviate dry air issues, which are common in colder months. This article explores the benefits of humidifier installation, types of humidifiers, and tips for proper setup.

Benefits of Installing a Humidifier

Improved Comfort: Humidifiers add moisture to the air, making your living space feel warmer and more comfortable, even at lower temperatures.

Health Benefits: Maintaining proper humidity levels can reduce respiratory problems, dry skin, and irritation in the eyes and nose.

Protection for Your Home: Proper humidity helps prevent wood furniture and flooring from cracking and protects artwork and musical instruments from damage.

Energy Efficiency: By maintaining comfortable humidity levels, you can feel warmer at lower thermostat settings, potentially reducing heating costs.

Types of Humidifiers

When considering humidifier installation, there are several types to choose from:

Portable Humidifiers: These are standalone units that can be moved from room to room. Ideal for smaller spaces, they are easy to set up and use.

Whole-House Humidifiers: Installed directly into your home’s HVAC system, these units provide consistent humidity throughout the entire house. They require professional installation but offer a more integrated solution.

Evaporative Humidifiers: Utilizing a fan and a wick, these humidifiers absorb water and release moisture into the air. They are self-regulating and less likely to over-humidify a space.

Steam Vaporizers: These units heat water to create steam, which is then cooled before being released into the air. They are generally less common for home use due to their energy consumption.

Installation Process

1. Assessment

A professional installer will assess your home’s layout, existing HVAC system, and specific needs to recommend the best humidifier type and size.

2. Selecting the Location

For portable units, choose a central location for optimal moisture distribution. For whole-house systems, the installer will determine the best integration point in your HVAC system.

3. Professional Installation

While portable humidifiers can be set up easily, whole-house systems typically require professional installation. This process includes connecting the humidifier to the water supply, ensuring proper drainage, and integrating it with your heating system.

4. Testing

After installation, the technician will test the unit to ensure it’s functioning correctly and adjusting humidity levels as needed.

Maintenance Tips

To ensure your humidifier operates efficiently, follow these maintenance tips:

Regular Cleaning: Clean the unit regularly to prevent mold and mineral buildup.

Change Filters: For units with filters, replace them according to the manufacturer’s recommendations.

Monitor Humidity Levels: Use a hygrometer to keep humidity between 30% and 50% for optimal comfort.

Conclusion

Installing a humidifier can significantly enhance your home’s comfort, especially during dry winter months. Whether you opt for a portable model or a whole-house system, the benefits of improved air quality, health, and energy efficiency make it a worthwhile investment. Consider consulting a professional for installation to ensure optimal performance and longevity. Enjoy a cozy, healthy indoor environment year-round!

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Weeping Tiles Calgary

Calgary, Alberta, known for its diverse climate, frequently experiences wet weather that can create challenges for homeowners. Weeping tiles, or foundation drainage systems, play an important role in managing excess water around your home's foundation. In this comprehensive guide, we'll explore the importance of weeping tiles, the services they offer in Calgary, and how they help protect your investment.

Weeping tiles, despite their name, are not actual tiles. They are a system of pipes installed around the perimeter of a building's foundation. These pipes collect groundwater and excess rainwater, carrying it away from the foundation to prevent basement flooding, water damage and structural issues. It is important for Calgary homeowners to understand how this system works.

Calgary boasts a number of rowing tile service providers that cater to the city's unique climate and terrain. These services typically include installation, inspection, repair, and maintenance of row tile systems. Certified professionals assess your home's specific needs, ensuring the system works optimally.

When installing weeping tiles in Calgary, professionals carefully plan the layout of the system, taking into account factors such as soil type and the local water table. Installation involves digging a trench around the foundation, laying a filter fabric, and laying weeping tiles. Precise installation is essential for long-term effectiveness.

The cost of rowing tile services in Calgary varies depending on factors such as the size of your property, the extent of repairs required and the choice of material. It is advisable to get multiple quotes and prioritize quality and reliability over cost alone.

Weeping Tiles Calgary services are important to protect your home from moisture related problems. Understanding the role of weeping tiles, recognizing the signs of problems and selecting the right service provider are important steps in ensuring that your home stays dry and structurally sound in Calgary.

[infoonwaterheaters]

A/c Unit Installation Service

A new ac unit is a vital investment for your house's comfort and also energy performance. It also can increase your residential property's value, specifically if it includes high-efficiency designs with a higher SEER score. It is necessary to pick a specialist who comprehends the a/c installation process as well as has experience in the area. This ensures that the system is installed properly as well as meets all safety codes. Here's a good read about tankless water heater furnace, check it out! Having the ideal company in mind will assist you locate the ideal system for your home as well as conserve you cash later on by maintaining your energy costs low and your system running successfully. To gather more awesome ideas on furnace cleaning calgary, click here to get started. First, a certified professional will certainly involve your residence for an initial assessment. They will gauge the area and compute the dimension of your a/c system. This allows them to give a quote and recommend the best design for your needs. As soon as the estimate has actually been supplied, it is time to get going with the actual installment. Typically, this entails getting rid of the old device and setting the new one on a pad. The brand-new unit must be positioned so that it will certainly cover most of the area of your house. If the ground is unequal, a gravel base might be utilized to ensure it is leveled correctly before the device is set in place. After the old system has actually been removed, electrical circuitry is separated from the system as well as the existing breaker box is shut off. Then, the service technician will certainly link the new device to your house's ductwork and include cooling agent, as directed by the producer. A solution detach will be changed near the air conditioning system, a safety gadget that can close the system down if it comes to be harmful. This detach includes specific locations where the circuit wires from the breaker panel will be connected and also a "whip" (versatile electrical channel) that carries the power to the system. Before setting up the air conditioning system, an accredited heating and cooling specialist will certainly test it to guarantee that it is running effectively. This is called appointing and is a vital action that several companies forget, however it is crucial to the wellness of your system. Depending on the type of a/c you have, this can include changing a coil or a filter, cleansing a condenser or transforming the hose pipes and drain lines. Having a licensed professional take care of these jobs can keep your a/c competing years ahead. If the a/c does not have a built-in air cleaner, a qualified specialist will install one. This prevents dirt as well as allergens from being launched into your home, and it can make your indoor air cleaner as well as much healthier. The installer will certainly after that run the copper hoses from the outside unit to the indoor device as well as secure them to the assigned places using the screws that included your unit. The cable televisions as well as pipes should be insulated to reduce the potential for them to bend and damage your device. During the setup, the technician will certainly make sure to inspect and change the vents as well as thermostat to ensure your residence is comfortable. They will also check for any kind of leakages that may create a trouble with your system. Kindly visit this website https://www.ehow.com/how_4853270_clean-kitchen-air-vents.html for more useful reference.

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Call experts to repair your Plumbing & Filter Systems

Looking for water softener repair in Calgary? Browse online sources that will help you get best water softener & Calgary water filter systems at affordable charges. They will make a visit at your place and let you know about the actual condition of your system! Try now!

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Furnace Repair

Right Diagnosis + Right Solutions Call for faster and fair priced repair services Accurate resolution at the very first visit 365 days emergency Furnace Repairs Calgary services Quickest Call-Outs for Repair and Replacement

(403) 498-7777

Furnace Repair Service in Calgary — available 24 hours

Regular Call-Outs with Best Repair Warranties

Get any type of furnace problem fixed at the lowest call-out and repair charges. We are just a single call away. Find support and solutions for all your queries for Broken Furnace Calgary repair and replacement.

24 x 7 Emergency Furnace Repair Services in Calgary

When it is about your comfort, there is no compromise. Call for our emergency service at any hour and any day including weekends and business holidays.

403-498-7777

No Suspense Over Repair Charges

We have applied our rich experience to let you know how much the repair will cost you. Our toll quickly draws out the precise repair charges to fix your furnace problem.

Finding out the issue and knowing the repair charge is a matter of few minutes. Call us and inform us how your furnace is behaving and we will let you know the options with repair price.

Alberta provides honest recommendations for replacement of existing units with new ones.

Call us for the Most Common Furnace Problems and Maintenance- 403-498-7777

Identify Common Furnace Problems and Avoid Repair

Sometimes a furnace does not work properly due to simple issues/mistakes that you can fix quickly. Before calling us, check the below list.

The unit is set to HEAT and not COOL The furnace is turned on properly Check the batteries The furnace filters are dirty and not changed at the interval of around 3 months Fixing these simple issues can help you save unnecessary call-outs for repairs Something (like debris, soil, and rodent) is accumulated in the furnace vent and restricting the air flow

Further, we have check-listed the issues that indeed require professional experts.

When You Should Call for Professional Furnace Repair Service-

Not all problems are just oversight mistakes. Do call us to get certified technicians for Furnace Repairs Calgary-

The furnace is switched on properly but not turning on The furnace is on but not giving heat or emitting very little heat Even after multiple tries, the pilot light is not turning on The colour of the pilot light is not as right Blower is constantly running Furnace goes off frequently on its own after turning on Unexpected or unusual noise from the unit Vent airflow is very weak Thermostat us not functioning properly You notice a sudden increase in your utility bill The furnace is experience water or gas leakage

Frequently Asked Questions

What is the cost of common furnace repairs?

Repair charges for the most common furnace issues cost from $180 to $350. In the case of failed parts like gas valve and motor, the total cost can be around and above $500. Call us for any type of Furnace Fix Calgary for long term solutions.

How much it costs to get a new motor for the furnace?

The total cost of new furnace motor with installation is approximately $500 and above. The cost is higher for the high-efficiency furnace; it will cost $1000 or more.

How do I know if I need to replace my furnace instead of getting repaired?

If the age of your furnace is less than 10 years and the repair are going to cost only half or less than new furnace, no need to buy a new one. If you are using the furnace for 10 or more than 10 years and repairs are costing more than third of the replacement, buying a new furnace is a right choice. Do consult for all your Furnace not Working Calgary.

When should I call for maintenance service for my furnace?

The heating system should be serviced yearly and especially before arrival of the long winters. Regular maintenance keeps the unit protected against major breakdowns.

How often should I change the filters?

If you are using one-inch low cost filters, do change them at least once in three months. High efficiency filters will last longer and need to get changed once or twice in a year. Proper change of filters gives you better air quality and cooling.

How can I keep my heating bills low?

Below simple tips can help you keep your heating bills low.

1. Get regular maintenance for the furnace from reputed Calgary Furnace Repair. 2. Change the filters as recommended. 3. Let the sunlight enter your house to keep warmer. 4. Seal the doors and windows properly. 5. Use an programmable thermostat.

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Science and Chemistry Classes

Carbon-capturing material could help industry reduce emissions and costs

by Michael Brown, University of Alberta

Alberta's world renown in carbon capture and sequestration is set to receive another lift thanks to the promise of a material invented and tested in the province that offers an efficient way to pull carbon dioxide out of industrial emissions. An team from the University of Alberta's Faculty of Engineering characterized a CO2   (CO.2) capturing microporous material developed by a group led by George Shimizu at the University of Calgary that attracts gas molecules and sees them stick to its surface. The material, named Calgary framework-20 (CALF-20), belongs to a family of microporous solids called metal-organic frameworks.Ph.D. student Tai Nguyen and Arvind Rajendran, associate professor in the U of A's Department of Chemical and Materials Engineering, tested the capabilities of CALF-20 to uncover its unique properties that make it an excellent candidate for CO2 capture. Rajendran explained that the idea behind metal-organic frameworks has been around for decades after researchers began proving that a combination of metals and organic molecules, known as linkers, had the potential of concentrating gases from a mixture.In the case of CALF-20, a single gram has a surface area of more than 500 square meters. These materials can be packed in a column, much like a catalytic converter, and essentially fastened to the end of a smokestack.Rajendran likens the process that follows when the emissions are sent through the material to a group of people being sent through a shopping district."You will start seeing that the people who don't like to shop move ahead, whereas those who do will move slower," he said."Initially, the people who don't like to shop come out first."In cases where the emissions are made up of nitrogen and CO2, the nitrogen comes out first while the CO2 is left behind, adhering to the material. To move the CO2 along so the material can be reused, either the pressure in the column is brought down and the concentrated CO2 is vacuumed out, or the system is heated up using waste heat or steam."When you provide heat, the CO2 is released and we can start collecting it in a more concentrated form than what you sent in."Solving practical problemsThe problem with these materials, however, is that while they often work in the controlled confines of a lab, they don't work in the presence of water or other impurities. That's where Rajendran's team stepped in."The innovation in this material is that it can handle water nicely. This means you don't have to dry your gas before you filter it through this material, which reduces the need for a whole bunch of energy," he said.Rajendran added that the experiments needed to characterize how materials perform in the presence of water are challenging and laborious: "We had to develop new techniques, and it took the enormous patience of Tai to demonstrate the exceptional ability of CALF-20 to concentrate CO2 even in the presence of water."The experiments Rajendran's team conducted were corroborated by a research team led by Tom Woo at the University of Ottawa using advanced molecular simulations.Another challenge for carbon-capturing materials is that even the tiniest quantities of emissions byproducts, such as sulfur dioxide and nitrous oxide, can kill the ability of these materials to capture CO2, Rajendran explained."The big advantage in CALF-20 is that it works under practical conditions for thousands of hours, where almost all other previous developments did not," he said.Once concentrated, the CO2 is either compressed and stored in geological formations, pushed back into old wells for enhanced oil recovery or converted back into fuel, such as methanol, to be used in the creation of other products.Reducing emissions and costsZoramat Solutions, a company based at the University of Calgary, scaled CALF-20 to the multi-kilogram scale, and Innovate Calgary licensed it to Svante, an industry partner out of Burnaby, B.C., that has developed a commercial process. Svante has shown that the material is suitable in an industrial setting and is now testing it in a cement plant at a capacity of one ton per day."This is possibly the first large-scale commercialization of a metal-organic framework," Rajendran said. "These are the next-generation carbon capture technologies that not only reduce CO2 emissions but reduce the cost. These innovations were made possible through multi-institution and interdisciplinary collaborations of synthetic and theoretical chemists, chemical engineers and industry."He added the timing coincides with the rollout of provincial initiatives to reduce industry's environmental footprint, including Canada's first hydrogen HUB launched in the Edmonton region, backed by more than $2 million in funding from three levels of government. The region is well positioned for success because it has one of the lowest hydrogen production costs in the world, existing experience in hydrogen production, a vast network of pipeline infrastructure, and suitable and existing sites for carbon capture—all of which are necessary to upgrade natural gas into hydrogen for use as a low-carbon fuel."In Alberta we sequester close to two to three million tons of CO2 every year and we have become a world leader in this technology because we have some of the biggest demonstration facilities in the entire world," Rajendran noted."The capability to develop new materials, associated processes and scale-up for industrial demonstration asserts Alberta's position as a world leader in carbon capture and storage."The research at the U of A was supported by an Alberta Innovates Strategic Research Program award and an NSERC CREATE grant.The study, "A scalable metal-organic framework as a durable physisorbent for carbon dioxide capture," was published in Science.

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Juniper Publishers-Open Access Journal of Environmental Sciences & Natural Resources

Impact of Sustained Discharge of Treated Wastewater Effluent on Wetland Water Quality

Authored by Roger Saint Fort

Abstract

This study investigated the impact on water quality of sustained discharge of treated wastewater effluent on the wetland commonly known as Weed Lake. A field sampling program was conducted during the months of May through September. Various physical, chemical, and biological analyses were performed on retrieved water samples. EC and TDS values increased both spatially and temporally from the south to the north quadrant of the wetland. Similar patterns were also observed for HPC and coliforms CFU enumeration. Turbidity and TSS decreased from May to June and then surged slightly while typically remaining constant from June to September. COD and TKN were found to decrease from May to July and to increase marginally from August to September. Potentially mineralizable nitrogen and phosphorous were ascertained as indices of the wetland sediment capacity for mineralizing both nutrients. Batch isotherms of PO4-3 were conducted for interaction determination with the wetland sediments.

The average value and standard deviation of potentially mineralizable nitrogen for the sediment samples was 15±12.92 mg/kg. Potentially mineralizable P was estimated at 29.67±11.96 mg/kg. The nitrogen pool of NH3-N in the wetland ecosystem was double the NO3-N pool. Langmuir data indicated an average maximum sorbing capacity of 190mg of PO4-3per kg of substrate. The value constants of maximum sorbing capacity ranged from 100 to 294mg of PO4-3 per kg of substrate. Total phosphorus concentration increased significantly from June to July and then decreased in September, these concentration changes were in parallel with algal and plankton blooms. Mass balance analysis indicated that 40 to 80% of phosphorous in Weed Lake is in various complex forms and not readily bioavailable. Labile-P and soluble-P represent a smaller fraction of the total-P. It appears that uncontrollable natural factors will have episodic and direct influence from year to year on the speciation of phosphorous and nitrogen in the wetland and influence also the spatial-temporal relationship status of its water quality. As a natural dynamic ecosystem, implementation and evaluation of best management practices should be continued together with subsequent evaluation.

Keywords: Water quality; Wastewater; Nutrient; Isotherm; Mass balance; Algae

Introduction

Weed Lake is a 6 km2 surface area of historic wetland and highly valued as an important natural feature within the community. Hereafter referred to as Weed Lake or wetland, its orientation is a south-north direction. The subject site is located 20 km east of the City of Calgary and northeast of the Hamlet of Langdon within the Municipality District (MD) of Rocky View No. 44 (Figure 1). Glenmore Trail and TransCanada Highway represent important access roads along the southeastern corner and the northwestern boundary of the Hamlet. Weed Lake was previously a healthy functioning wetland ecosystem characterized by important waterfowl production, breeding habitat and staging area for a large number of shorebirds in transit during migration. The wetland was drained in 1971. However, because of a variety of soil fertility problems, the expected agricultural benefits of draining the original wetland were never achieved.

A Restoration and Rehabilitation Program were initiated in 2006 to restore Weed Lake as a dynamic and fully functioning wetland ecosystem. Currently, Weed Lake is a productive ecological aquatic environment that hosts a variety of aquatic plants, namely: emergent aquatic vegetation, floating leaved plants, submergent aquatic plants and free floating plants. The climate of the area is described as being largely sub-continental characterized by short and moderately warm summers, brief spring and fall seasons. The winter is rather long. The ambient temperature typically ranges between -350C and 250C. Average annual precipitation is approximately 55 cm. The surrounding land uses around the wetland is primarily agricultural comprising mainly of farmstead parcels and un-fragmented quarter sections [1].

The soils of Weed Lake were classified as Rego Gleysols and the major portion of the upland as Solonetznic soils [2]. These soils, while high in soluble salts and sodium, are predominantly heavy glacial tills to clay loam. Soils in the dipressional areas are classified as Rego Gleysols and were developed in fine textured, lacustrine sediments. Weed Lake area is generally flat consisting of sections sloping gently from the west toward the lake at an approximate rate of 0.25%. The upland landscape is gently undulating. Two major depressional areas exist in the center of each SE and NW portions of Weed Lake TP 23 R27 W4. In some areas, the banks of Weed Lake provide a sudden and discernible drop in surface topography. Weed Lake received a constant source of tertiary wastewater effluent influxes from the Hamlet's wastewater treatment facility during the spring, summer and fall seasons. The wetland shore line is relatively flat with the lake depth being less than 1.20 meter over much of its area. Typical annual water level varies from 76 to 55 cm.

Storm water from the Hamlet flows into the lake through a network of major and minor ditch systems. Influx of storm water from the Balzac area also flows into Weed Lake and is routed through the main drainage ditch through the Hamlet. The former may carry considerable amount of sediments and salts, especially in the spring season. Irrigation water is in some instances supplemented to stabilize the wetland water level during periods of drought. Flows out of the wetland are controlled by an outlet located east of the wetland and is mainly drained by Rosebud Creek. The main objectives of this study were to ascertain Weed Lake water quality through the months of May to September, and to gain insights into the relationship between basic physicochemical and biological processes. Hence, the impact on water quality of sustained discharge of treated effluent in Weed Lake can be scientifically evaluated.

Materials and Methods

Weed Lake Surface Water Sampling

The wetland was sampled once a month through the months of May to September. Representative grab samples were retrieved from five sampling locations and their respective global positioning system (GPS) coordinates recorded. Subsequent sampling of the wetland was achieved based on each sampling location precise and unique identifier. All water samples were collected in one liter sterilized glass bottle at depth of 12 cm below the surface water level. The process involved lowering the capped bottle into the water column at the desired depth. The cap was then removed to allow water collection. Once filled, the bottle was capped, brought to surface and appropriately labelled. The water samples were then transported in Calgary and kept refrigerated at 70C for subsequent chemical and physical analysis. Field measurements of water temperature, dissolved oxygen (DO), and water level were performed at each sampling location at sampling time.

The remaining physical, chemical, and biological parameters were performed in the laboratory. Water samples for bacteriological analyses were collected from each sampling location in labeled, 50 mL sterile containers and brought back to Calgary. The sterile containers were transferred into a cooler for transportation. The cooler temperature was maintained at 50C. The samples were then serially diluted and incubated within 3 hours after sampling.

Weed Lake Potentially Mineralizable -Nitrogen (PMN) and -Phosphorous (PMP)

The process involved placing 10 g of air-dry substrate into a 150 mL acid washed Pyrex flask to which 25mL of 0.01mL CaCl2 was added [3]. The suspension in the flask was gently mixed, weighed, capped with Al foil and placed in the autoclave overnight at 1210C and 1500 kPa. Then, the flask and its contents were allowed to cool to room temperature, weighed, and quantitatively adjusted with deionized water. The mixture was transferred in centrifuge tubes and spun for 4 minutes at 4500 RPM and the liquid filtered through Whatman No. 2 filter paper. The difference between the autoclave treatment and the NH3-N, NO3-N and PO43 initially present in the substrate indicates the NH3-N, NO3-N and PO4-3 produced by autoclaving.

Weed Lake Batch Isotherm of Orthophosphate

To carry out the isotherm study, six sediment samples were collected from the bottom of the wetland using a hand Dutch auger. The substrates were transferred in one liter wide mouth glass jar, accordingly labeled and stored in the fridge at 40C. Prior to initiate the batch isotherm study, the samples were allowed to equilibrate with the room temperature. Batch testing was used to obtain the equilibrium sorption capacity of a given sediment sample for a corresponding concentration of phosphorous (PO43). This was achieved by developing equilibrium isotherms that describe the sorption capacity of the sediment exposed to various concentrations of aqueous solutions of PO43. Batch studies were conducted by gently mixing a specific amount of the sediment substrate with a specific volume of PO4'3 solution. The latter was prepared with deionized water. Each sorbate/sorbent system was then allowed to equilibrate overnight at room temperature and 80C, respectively. Following equilibration, the suspension was centrifuged at 5000 RPM for 4 minutes.

The supernatant from each system was retrieved and analyzed for the construction of the isotherms. The extent of PO4'3 sorption was estimated as the difference between initial concentration of PO4'3 and final concentration at equilibrium. Corrections were made for PO43 present in the original substrate.

Weed Lake Material Balance Analysis

Several assumptions were made in assessing Weed Lake, being a dynamic system with finite capacity to cope with anthropogenic inputs which can affect its intrinsic quality. A steady state equilibrium conditions exists between precipitation and evaporation,

a) A steady state equilibrium conditions exists between upward capillary groundwater movement and seeping water,

b) Outgoing water released through the gate doesn’t represent a significant enough volume of water to disturb the overall equilibrium status of Weed Lake under current water management,

c) Incoming water from any tributary doesn’t represent a significant enough volume of water to disturb the overall equilibrium status of Weed Lake,

d) The rate of organic matter decay in relation to nutrient mineralization are in equilibrium interaction with uptake by the aquatic vegetation and growth dynamics,

e) Lateral averaging assumes longitudinal and vertical hydrodynamics variations in velocities, constituents, water density, and temperature are negligible,

f) Sediment oxygen demand (SOD) is coupled to the water column dissolved oxygen.

Water quality interactions are by necessity simplified for descriptions of most aquatic ecosystems that are intrinsically complex. Hence, Weed Lake can be scientifically analyzed with considerable flexibility as a steady-state conservative system without any potential technical limitations of great significance. Based on Weed lake geometry and boundary, the major perturbations affecting the Lake hydrodynamics and quality during the investigated months of May through September are created primarily by wind and temperature induced circulation. In that regard, to a lesser extent by hydraulically induced turbulence and circulation. Wind causes Weed lake water column to be mixed through circulatory motion that extends to the bottom. This echoes the technical sentiment that complete water mixing occurs in the wetland boundary within a timeframe of 10 days. As a result, temperature differential between surface and bottom heat exchange is therefore considered conservative.

Analytical Program

*Not applicable; “Chemical oxygen demand; bTotal suspended solids; cTotal dissolved solids; "Dissolved oxygen; eSodium absorption ratio = {[Na/([Ca + Mg]/2)1/2}

The analytical testing program along with the associated quality assurance and control (QA/QC) for the study are depicted in Table 1. Standard recommended holding times were followed for the samples. Bacteriological analyses were performed on water samples collected in sterile jars. Serial dilutions were accordingly performed on the water samples. Subsequently, the diluted samples were incubated using the recommended Millipore media pad for heterotrophic plate count (HPC) and Escherichia coli (E. Coli) & Coliform organisms. The number of colony forming units (CFU) were enumerated and recorded.

Results and Discussions

Weed Lake Potentially Mineralizable Nitrogen (PMN) and Phosphorous (PMP)

The results of PMN as an index of potential mineralization of organic nitrogen to inorganic nitrogen forms of NH3-N or NO3-N are reported in Table 2. Reactive P initial present in these substrates were also evaluated and are reported in Table 3. The data indicate that the substrate found at the bottom of Weed Lake has the potential to contribute to the inorganic pools of N that is present in the water column. Total Kjeldahl nitrogen (TKN) which refers to the combination of ammonia and organic nitrogen ranged from 30 to 1.97mg/L likely contributes significantly to the mineralizable N pool. The average value and standard deviation of PMN for the six samples were 15±12.92 mg/kg while potentially mineralizable P was estimated at 29.67± 11.96mg/kg. Ratio of NH3-N/NO3-N was calculated for each autoclaved substrate and was found to oscillate around a ratio value of 2.

NA=Not applicable.

Therefore, the potential reserve of NH3-N in the wetland pool of PMN and PMP will vary with temperature, plants density, ecosystem is twice more than NO3-N. The dynamic and fate ofthat dissolved oxygen level, water level. Degree of hydrodynamicmixing of mineralized N is expected to be primarily driven by wind conditions. The results further indicate the presence of a pool of PO4'3 in the bottom boundary of the wetland. That pool is relatively bio-available for uptake by the aquatic plants that comprise Weed Lake ecosystem.

Weed Lake Batch Isotherm Study of Orthophosphate

Sorption isotherms are normally obtained by measuring the amount of solute sorbed for a number of different concentrations of sorbate under specific conditions. They often can be described by the Freundlich or Langmuir equations. The Freundlich isotherm, a commonly used curvilinear model has no upper limit to the amount of sorbate that could be sorbed by a system. The Freundlich equation, Equation (1) can be written as:

where X/M is the quantity of PO4'3 sorbed per unit mass of sediment (mg/kg), Ceq is the equilibrium concentration of PO4'3 in the solution (mg/L) and where Kd and n are the constants. The logarithmic form of the Freundlich equation to plot the data is shown in Equation (2):

The logarithm of the concentration of the solute in the sorbate state, X/M in mg/kg, is plotted as a function of the logarithm of the residual solute concentration, Ceq in mg/L. Linear regression of the data points yields a best-fit line with a slope of 1/n and intercept of log [Kd]. The slope, 1/n, is a measure of sorption intensity, and the Kd value, which must be determined by taking the antilog of the intercept, is the partition coefficient, an indicator of the sorptive capacity of the system. A Langmuir plot models a system where there are a finite number sorption sites. The Langmuir equation, Equation (3) may be expressed as follows:

Where X/M and C are the same units as defined above, bis a constant related to the binding energy (L/kg), and a is the maximum amount of solute that can be sorbed by the sorbate, is the soil uptake quantity (mg/Kg). The Langmuir equation can be rewritten in the following linear form shown in Equation (4):

[Ceq]/[X/M] can be plotted as a function of Ceq. The linear regression of the data points yields a best-fit line with a slope of 1/a and 1/ab as the intercept. The maximum amount of PO4'3 that can be sorbed onto the samples can be calculated from the Langmuir linear equation.

The isotherm models coefficients for the representative equilibrium studies are summarized in Table 3. The regression equations and the corresponding coefficient of determination (R2) are given in Table 3. It appears that the P sorption data of solution could be best described mathematically by the Langmuir equation. In this current case, the Langmuir data indicate that the Weed Lake sediment has an average maximum sorbing capacity of 190 mg of PO43 per kg of substrate. The value constants of maximum sorbing capacity ranged from 100 to 294 of PO4'3 per kg of substrate which reflect the heterogeneity in the composition of the sediment substrate. Therefore, the sediment substrate serves as a significant sink for PO4'3 as long as the sorbing capacity is not exceeded nor the pH becomes basic. The latter case has not been observed throughout the duration of the monitoring program.

Weed Lake Water Monitoring

The trend in water quality status of the wetland was compiled in Table 4 in a comparative summary as average values for the parameters tested for years 2009 to 2016, respectively. Under the objectives of this research project, the parameters were compared to current Surface Water Quality Guidelines for Use in Alberta with respect to Freshwater Aquatic Life for long term [4]. The guidelines are numerical concentrations or narrative statements recommended to support and maintain a designated water body. The wetland was scientifically analyzed with flexibility as a steady-state conservative system with limited potential technical limitations of meaningful significance. Based on its geometry and boundary, it is deduced that the major perturbations affecting the hydrodynamics and water quality during the investigated months are created primarily by wind and temperature-induced circulation and to a lesser extent by hydraulically induced turbulence and circulation.

aTurbidity Guideline; bTSS Guideline; cDO Guideline; dLake Temperature Guideline.

Wind causes water column mixing through circulatory motion that likely extends to the lower boundary of the water column. Complete mixing of the wetland water is conceived to occur within a time frame of ten days. As a result, temperature differential between surface and bottom heat exchange is considered conservative as well as spatially throughout the water mass. Observed temperature difference, AT, is less than 20C, both in the water column and spatially, irrespective of the sampling month. Temperature differential between surface and bottom heat exchange is considered conservative [5]. As expected, the importance of hydraulic, thermally, and wind- induced circulation in active interactions and combinations in bringing about dynamic changes in Weed Lake water quality varies depending on the specific parameters. Analysis of water quality indicators show that some parameters are more affected in varying degree in their distribution pattern with respect to spatial and seasonal variations.

Data spatial variability within a sampling event appears not to be significantly different from one sampling point to the next. Annual recorded chemical and physical parameters for grab samples tend to marginally increase spatially and temporally with corresponding standard errors ranging from 1.3% to 15%. This supports the assumption that complete mixing of Weed Lake water column is enhanced through wind induced circulation patterns which negate the geometry effects in inducing intrinsic spatial variability. Biological parameters of HPC-total and E. coli & Coliform colony forming unit (CFU) enumeration tend to decrease from the south to the north quadrant of the wetland. The south quadrant is where the pipe discharges treated effluent from the wastewater plant into the wetland.

Enumeration of CFU for both biological parameters spatially appear to vary randomly, hence no discernible pattern could be denoted. However, the level of CFU enumeration tends to increase with temperature. The lowest level of bacteria and coliform organisms are typically denoted for the months of May and September. CEC and TDS values tend to increase both spatially and temporally from the south to the north quadrant. This could be best attributed to influxes of storm water diverted into the wetland. Turbidity and TSS generally decreased from May to June and then marginally increased to remain constant from June to September. COD and TKN typically decreased from May to July but slightly increased from August to September. The trend observed in relation to turbidity, TSS, COD and TKN clearly reflects the combining effects of hydrodynamic mixing with a high degree of photosynthesis and metabolic synergistic relationships between algae and bacteria.

Furthermore, when ascertaining the trend in the data for the average parameters from years 2009 to 2016 (Table 5), a pronounced difference can be observed. Both spatial and temporal variations can be best corroborated to operational changes, natural factors, and seasonal variations. These factors will interact to accordingly create new episodic dynamic equilibrium in the wetland functional systems. According to Table 5, the trend in values for pH, DO, and water temperature remained the most relatively stable as denoted by their respective standard deviation and standard error. The overall stability of the pH is also a good indication of the wetland buffering capacity. Functionally, the ability to resist change in pH can be attributed to the presence of CO2, CO3-2, HCO3- and organic matter whose origins are primarily of natural sources and from operational activities (i.e., wastewater effluents) to a lesser degree. Given the presence of decomposable organic materials at the bottom of the wetland, the following reduction processes may be occurring. They may naturally further sulfate-enrich the water chemistry and contributing to the buffering capacity as depicted in Equation (5) and Equation (6):

The presence of dissolved oxygen is of fundamental importance in maintaining aquatic life and the aesthetic quality of Weed Lake. Because of this importance, oxygen can be regarded as one of the most important water quality parameters.The impact is measured as oxygen demand, a parameter that can be interpreted as a gross measure of the concentration of oxidizable materials present in the water column and as a status of potential organic load. Through the metabolic action of bacteria, organic material (OM) in the water column is oxidized to its lowest energy state through the following mechanisms, Equation (7):

Dissolved oxygen profile in the water column tends to increase from the months of May to June (representative average 8.94 mg/L) and then drastically decrease during July and August (representative average 4.07 mg/L) to subsequently route to a marginal increase in September (representative average 6.42 mg/L). No stratification of dissolved oxygen was denoted in the water column during any of the monitoring programs. Dissolved oxygen at the bottom-water interface was totally lacking, therefore making it an anaerobic, organic matter rich boundary in the wetland. Above the anaerobic substrate layer, an intermediate transition zone was not identified which contained dissolved oxygen. Following episodic discharge of treated wastewater effluent, its mixing through the water column, and after some time has elapsed, several changes occurred.

The various inter and intra relationships between wind action, temperature, precipitation, and sunlight are germane to the wetland intrinsic stabilization processes. In that regard, these factors are natural and not controllable. Based on dissolved oxygen readings, stabilization reactions appear to be aerobically dominated. During the stabilization processes, much of the biodegradable organic matter pool is transformed by bacteria into living organic matter. As a by-product of their metabolism, they release through mineralization into the water column CO2, nitrates, phosphates, sulfates, and other mineral salts. A conceptual framework depicted in Figure 2 provides a fundamental representation of physicochemical and biological dynamics occurring in the wetland. Such conceptual model would aid in long-term nutrient mass balance monitoring and developing a better understanding of nutrient systems behavior.

Aerobic stabilization is highly influenced by the hydrodynamic mixing created by wind action, temperature, and sunlight. However, at lower temperature like during the months of April, May, and October, the overall biological activities and therefore, the stabilization processes in Weed Lake are slower. Consequently, the algae level remains relatively low. As temperature of the wetland water column increases, this triggers in response higher algae metabolic activity. Under the additional favorable natural conditions of peak solar radiation during the months of June and July, algae proliferate. They absorb light and use the mineralized by-products during this highly photosynthetic period. Their cellular material releases oxygen in the water column, often giving rise to supersaturated conditions in some instances. Furthermore, the combination of high temperature, dissolved oxygen and solar radiation as well as the quick stimulation of bacterial activity enhance oxygen consumption.

This therefore stimulates blue-green algae (Cyanophyceae) to grow exponentially relative to the more efficient green algae (Chlorophyceae). As a result, heavy algal blooms are observed in the wetland with thick green mats appearing on the water surface. From this point on, anaerobic conditions arise, the column water is typically turbid and objectionable anaerobic odours are produced and released. The month of August typically produces anaerobic conditions as evidenced by dissolved oxygen average concentration of 2.73 mg/L. Since algal oxygen production is a direct function of photosynthesis, a gradual decrease in water temperature will be accompanied by decreased algal activity and therefore lower oxygen production. Consequently, the floating green mats on the water surface impair light penetration. Consequently, decreased photosynthesis in deeper portions of the water column results in decreased oxygen production together with a decrease in algal activity.

Under these conditions, wind action doesn't mix the water mass sufficiently to transport oxygen from the surface to the lower layers. At this point, the algal mass starts dying off, decaying through induced microbial decomposition, which results in the settling of biomass to the bottom boundary. This leads to the development of an organic layer of substrate that works as an anaerobic digester. It is noteworthy that this chain of events represents the natural ecological order and stabilization processes in the wetland. The COD test was used to ascertain the organic carbon content. Unlike biological oxygen demand (BOD), the COD test does not differentiate between biologically oxidizable and inert organic matter. Based on the overall trend in the data analysis, COD values tend to decrease from May to June as well as July but the COD values then increase or decrease from June to July and tend to increase during the months of August to September.

Typically lower DO readings are observed in July and August because of the past presence of higher level of oxidizable materials in the water column. Minimal DO stratification was observed throughout the depth of Weed Lake indicating significant longitudinal and vertical hydrodynamics mixing in the water column. Anoxic characteristic of the wetland in May results in some degree of objectionable odor as a result of bacterial reduction of NO3-, SO42, NH3-N, and other products of bacterial growth. Algae growth was more abundant during the months of May to July but significantly decreased during the months of August and September. Depicted in Tables 6-10 is the ratio of total-P/NH3-N for the wetland water column and treated effluent as well as the ratio for PO43/NH3-N for selected representative years. The ratios can be used as an important determining factor in assessing on an ongoing basis the management of the water quality with respect to effluent influxes and episodic water release from Weed Lake.

Main Nutrients Budget Analysis

The wetland aquatic environment is the host for a variety of aquatic plants namely emergent aquatic vegetation, floating leaved plants, submergent aquatic plants and free floating plants. The months of May to September mark the periods of active microbial and aquatic growth in Weed Lake. The data indicate that in order to maintain proper water quality and managing algal bloom as well as potential offensive odor, particularly for the critical months of July and August, it would be prudent to maintain a treated effluent discharge with a ratio of total-P/ NH3-N around 0.55. However, an effluent ratio of total-P/ NH3-N between 0.55 and 1.45 should be effectively adequate in maintaining proper water quality of the wetland.

A significant improvement in the wastewater treated effluent quality has been observed from the data recorded between the years 2010 to 2014. The results indicate for the year 2014 a treated effluent ratio of total-P/NH3-N ranging from 0. 05 to 0.74 and a water column ratio of PO43/NH3-N varying from 0.14 to 0.23. With respect to year 2010, the treated effluent ratio of PO43/NH3-N oscillated between 0.13 and 1.22 while the water column ratio of PO4-3/NH3-N varying from 0.26 to 1.02.

Variations in those ratio values were the norm for the other comprising monitoring years. Consequently, the water column ratio of total-P/NH3-N and PO4-3/NH3-N significantly improved from 2010 to 2014. The water column ratio of total-P/NH3-N in 2014 was established to range from 0.30 to 1.88 while it was from 1.07 to 2.68 in 2010. Furthermore, in 2014, the water column ratio of PO43/NH3-N ranged from 0.14 to 0. 23 compared to year 2010 in which case it ranged from 0.26 to 1.02 (Table 7).

In a manner similar to nitrogen, phosphorous in the wetland is expected to cycle between organic and inorganic forms. However, phosphorous unlike nitrogen doesn't cycle as a gas. It has to be assumed that labile-P, the not so strongly sorbed intermediate form by the wetland sediment, represents a smaller fraction of total-P. It may enter in equilibrium with soluble-P to increase the level of orthophosphate in the wetland water column. Hence, the material balance constructed for phosphorous is orthophosphate and will be considered as the only form of phosphorus that is readily used by any aquatic plants and microorganisms in the wetland ecosystem. Therefore, significant amount of orthophosphate is removed through algal and macrophytes growth but more significantly during the months of May, June and July. As result keeping orthophosphate concentration relative low throughout the wetland ecosystem boundary.

Concurrently, conversion of dissolved forms of phosphorus into insoluble forms such as calcium phosphate Ca3(HPO4)2, magnesium phosphate Mg3(HPO4)2, and ferric phosphate FePO4 and AlPO4 complexes will contribute to the removal and control of PO43 concentration level as well as to controlling its buffering capacity. Additionally, phosphorous bioavailability may be significantly affected through organic complex formation with humic and fulvic acids. Given the water pH being greater than 8.50, assumptions must also be made regarding the activities and contribution of Al retention of PO43 onto the sediment as AlPO4 complex. The later complex will be closely related to the contents of acid-extractable Al+3 in the sediment. Total phosphorus (i.e., P-inorganic and P-organic) concentration increased significantly from June to July to decrease in September which parallels algal and plankton blooms (Table 8).

Weed Lake Material Balance Analysis

A simple water budget approach was used to analyze the water level dynamics in Weed Lake Equation (8):

A simple water budget approach was used to analyze the water level dynamics in Weed Lake Equation (8):

R = Volume of present in the wetland at any time,

Pr =Annual precipitation,

Inwt = Incoming water from the wastewater treatment plant, Tr = Tributaries feeding into the wetland,

Ca = Capillary groundwater feeding the wetland,

E = Evaporation of water from the wetland,

vap r '

Se = Seepage water from the wetland,

Out canal = Water released in the canal via the gate.

Therefore, the above water budget equation for the wetland can be simplified and rewritten as Equation (9):

Of special significance to the wetland water quality management program are nitrogen and phosphorous. The interrelationships that exist between these two nutrients are best manifested in their fundamental importance in eutrophication. A mass balance analysis was performed for phosphorous and nitrogen, both being the nutrients of greatest input from the wastewater effluent being regularly discharged into the wetland. The following assumptions were derived in formulating the mass balance analysis for nitrogen and phosphorous (Tables 9,10). Assumptions made for nitrogen:

i. Biological conversion of organic-N ---> NH3-N is not significant from November to April

ii. Mineralization of NH3-N ---> NO3-N is not significant from November to April

iii. Biological reduction of NH3-N ---> NH3 (g) is not significant from November to April and, assumptions for phosphorous:

iv. Biological conversion of organic-P --->PO43 is not significant from November to April

v. Formations of insoluble forms of Ca (HPO4)2 and Mg (HPO4)2 are nominal relative to the overall process of soluble PO4-3 removal by microorganisms, algae and plankton.

vi. Equilibrium reaction exists between soluble PO43 <---> sediment sorbed PO4'3

vii. The material balance equation for can be written Equation (10) for each nutrient of interest:

Total-P, PO4'3and NH3-N are expected to undergo significant biotic and abiotic interactions during the months of May to September. Their decay rate could be modeled as a first-order reaction Equation (11). That is

where K is the reaction rate coefficient with dimensions of 1/ time and C is the nutrient concentration. According to Equation (11), the rate of loss of any of these nutrients is proportional to the amount of available substance that is present in the water column. The integrated first order rate law yields Equation (12):

where C is the initial concentration of NO-N or PO'3 at first

The regression equations for rate constant, K, determination of NO3-N and PO43 for selected years were derived for the wetland most biologically active period (Table 11). Assuming that both nutrients are uniformly distributed throughout the wetland water column, hence the total amount of a nutrient is calculated as CV according to Equation (14). Thus,

where C represents the concentration of nutrient and it is uniformly distributed throughout the volume, V, of the wetland water column. The material balance becomes Equation (15):

Monthly phosphorous and nitrogen load (MLP or N) as a result of effluent discharges can be calculated Equation (16):

Where, EmV represents monthly volume of effluent (L) and CE, effluent concentration (mg/L). Therefore, average volume of water (LV) in the wetland at sampling time Equation (17):

The mass balance analysis reveals a decreasing trend in nutrients level in the wetland. In 2012 the water matrix consisted of 45% of PO4-3 which translated into a load of 1.32 x 106 g with a corresponding load of 8017g of NH3-N meaning a ratio of PO4-3/NH3-N of 165:1. Concurrently, 55% of phosphorus can be assumed to be in the forms of condensed-phosphates and organically bound-phosphates which represent a load of 1.63 x 106g. With respect to 2013, the wetland water matrix was made up of 35% PO43. Which translated into a load of 1.34 x 106 g with a corresponding load of 1.6 x 105 NH3-N. Hence 65% of phosphorous in the water mass can be assumed to be in complex forms. For year 2014, it was determined that 82% of phosphorous status was in various complex forms. The direct impact of various uncontrollable natural factors will influence the speciation of phosphorous and nitrogen in Weed lake from year to year.

Nonetheless, if too much nitrogen enters the wetland through effluent discharge to offset the current nutrient ratio PO4-3/NH3-N, the result will likely be rapid and significant growth of aquatic vegetation in nuisance quantities and eventually lowering DO content due to the death and decay of the aquatic vegetation. As a natural dynamic system, implementation and evaluation of best management practices of Weed Lake should be continued and accordingly evaluated in order to strive to achieve and maintain a healthy wetland ecosystem.

Conclusion

The results of the Weed Lake water quality monitoring program study indicate spatial and temporal variations in the concentrations of the parameters tested. EC and TDS values tend to increase both spatially and temporally from the south to the north quadrant. Similar trend has been observed as it relates to HPC and coliforms CFU enumeration. Mass balance analysis indicates that 40 to 80% of phosphorous in the wetland water column is in various complex forms. Uncontrollable natural factors will have a direct influence from year to year on the speciation of phosphorous and nitrogen in the wetland ecosystem. Any surges or significant departure from the current nitrate inputs will have the potential to adversely affect the water quality and health of the wetland.

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Pre-Cleaning Preparation Check-List We Follow

Inspect the furnace for normal functioning Check the UV light, damper, humidifier Cover the home floors with cloths for protection Apply corner protectors

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Does cleaning increases the efficiency of the products?

The main purpose of cleaning is to remove all the debris and other objects from the ducts. The obstructions impede the airflow which causes strain on the system. Untidy components like coils and handlers also decrease the efficiency of the furnaces.

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Duct cleaning does not cause any damage to the vents or the system. However, contact only a reputed Furnace Duct Cleaning Calgary company for cleaning. A reckless cleaner may cause damage to your home during the cleaning. We take proper care for the safety of your furniture and floorings while cleaning.

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New Post has been published on https://freenews.today/2021/03/07/are-there-mussels-on-your-moss-balls-alberta-officials-warn-of-tiny-invasive-species/

Are there mussels on your moss balls? Alberta officials warn of tiny invasive species

CALGARY — Wildlife officials are sounding the alarm following the discovery of a tiny invader that hitched a ride into Alberta last week.

Moss balls, also known as marimos, are a popular item among aquarium lovers and are sold in many pet and plant stores throughout the province.

However, when provincial officials discovered a delivery of moss balls to an Alberta distributor had stowaway on board, they became concerned.

“Staff inspected the moss balls and confirmed that invasive mussels were found,” Alberta Environment and Parks wrote on Facebook.

The intercepted shipment originated from the Ukraine, the same place where a number of U.S. businesses also received the contaminated moss balls.

Zebra mussels pose “a significant threat” to Alberta’s waterways, the province says, especially because they are extremely difficult to eradicate.

“Invasive mussels are filter feeders that strain suspended matter and food particles out of the water, disrupting natural food chains and leading to a depleted fishery (fewer and smaller fish) as the fish don’t have enough food,” a government document reads.

All of the moss balls in the shipment were seized under the Fisheries Act, officials say.

(Supplied/Alberta Environment and Parks)

Meanwhile, any aquarium owners who’ve recently received moss balls through the mail are encouraged to inspect them for any zebra mussels that may have hitched a ride.

“Inspect your moss balls for invasive mussels both visually and by feeling for hard shells. Remember – they can be very small!” the province says.

Anyone who believes they may have found any mussels are encouraged to call the 24/7 hotline at 1-855-336-2628.

Residents should place any infested moss balls they find into a sealable plastic bag and freeze them for at least 24 hours. The moss ball, along with all of its packaging, must then be thrown into the garbage.

“Please do not flush moss balls down the toilet or dispose of them in the compost,” officials say. “Invasive mussels pose a serious threat to Alberta’s aquatic ecosystems, fisheries and water infrastructure like irrigation canals. Never dump aquarium tank pets, plants or water into any residential water system or Alberta waterway.”

(Supplied/Alberta Environment and Parks)

Zebra mussels, which can produce about one million eggs each year, do not possess any natural predators in Alberta.

The province says if a mussel infestation occurred here, it would cost $75 million per year to repair the damage caused to waterways, infrastructure and lost revenue from recreational fishing.

⚠️Invasive mussels have been found in moss balls being sold in Alberta. We need you to take action to prevent the introduction & protect our waters from this invader! Call our 24/7 hotline at 1-855-336-2628 if you find a mussel in your moss ball. Read more https://t.co/h57myUMGHO pic.twitter.com/j6VLD31eDl

— Alberta Environment (@AB_Enviro) March 6, 2021

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Meena Rezkallah, P.Eng.

Sep 11

1 min read

Water and Wastewater Industry

Updated: Nov 22

Meena Development LTD. has a long history of water and wastewater projects and clients. We provide multidisciplinary engineering services (piping stress analysis and structural engineering) to water and wastewater clients in need of maintenance, repair and building structures that control water flows and resources. Existing clients utilize Meena Development LTD. for industrial wastewater treatment and disposal, industrial water supply, municipal wastewater treatment and water distribution.

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Sometimes a furnace does not work properly due to simple issues/mistakes that you can fix quickly. Before calling us, check the below list.

The unit is set to HEAT and not COOL The furnace is turned on properly Check the batteries The furnace filters are dirty and not changed at the interval of around 3 months Fixing these simple issues can help you save unnecessary call-outs for repairs Something (like debris, soil, and rodent) is accumulated in the furnace vent and restricting the air flow

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Not all problems are just oversight mistakes. Do call us to get certified technicians for Furnace Repairs Calgary-

The furnace is switched on properly but not turning on The furnace is on but not giving heat or emitting very little heat Even after multiple tries, the pilot light is not turning on The colour of the pilot light is not as right Blower is constantly running Furnace goes off frequently on its own after turning on Unexpected or unusual noise from the unit Vent airflow is very weak Thermostat us not functioning properly You notice a sudden increase in your utility bill The furnace is experience water or gas leakage

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What is the cost of common furnace repairs?

Repair charges for the most common furnace issues cost from $180 to $350. In the case of failed parts like gas valve and motor, the total cost can be around and above $500. Call us for any type of Furnace Fix Calgary for long term solutions.

How much it costs to get a new motor for the furnace?

The total cost of new furnace motor with installation is approximately $500 and above. The cost is higher for the high-efficiency furnace; it will cost $1000 or more.

How do I know if I need to replace my furnace instead of getting repaired?

If the age of your furnace is less than 10 years and the repair are going to cost only half or less than new furnace, no need to buy a new one. If you are using the furnace for 10 or more than 10 years and repairs are costing more than third of the replacement, buying a new furnace is a right choice. Do consult for all your Furnace not Working Calgary.

When should I call for maintenance service for my furnace?

The heating system should be serviced yearly and especially before arrival of the long winters. Regular maintenance keeps the unit protected against major breakdowns.

How often should I change the filters?

If you are using one-inch low cost filters, do change them at least once in three months. High efficiency filters will last longer and need to get changed once or twice in a year. Proper change of filters gives you better air quality and cooling.

How can I keep my heating bills low?

Below simple tips can help you keep your heating bills low.

1. Get regular maintenance for the furnace from reputed Calgary Furnace Repair. 2. Change the filters as recommended. 3. Let the sunlight enter your house to keep warmer. 4. Seal the doors and windows properly. 5. Use an programmable thermostat.

Furnace Repair Calgary, Broken Furnace Calgary, Furnace Repair Services in Calgary, Calgary Furnace Repair, Furnace Repair Services Calgary

[anamorales]

057: Digestive health and building a healthy immune system with Dr. Melina Roberts

Hi friends! I’m so excited to have Dr. Melina Roberts on the podcast this morning. She was so knowledgeable and I really enjoyed our conversation. I hope you love this one!

Here’s what we chat about on today’s episode: 

Tips for promoting a healthy immune system, especially with everything going on and as we head into the winter months

Go-to supplements

Alkaline water or regular filtered water?

Importance of digestive health and tips for promoting healthy digestion

Her experience with cancer therapy and things we can do to protect ourselves as we continue to age

And so.much.more.

Here’s a little bit more about Dr. Melina Roberts:

Dr. Melina Roberts is a Naturopathic Doctor, Author of Building a Healthy Child and Founder of Advanced Naturopathic Medical Centre in Calgary. She is recognized as one of the top Biological Medicine practitioners in North America and is a lecturer for the Paracelsus Academy. She is a leading authority in the field of naturopathic medicine specializing in Biological Medicine effectively treating digestive issues, chronic disease and cancer. Dr. Roberts is a graduate of the University of Waterloo and the Canadian College of Naturopathic Medicine in Toronto. She did a 2 year post-graduate study in Biological Medicine with Paracelsus Klinik in Switzerland. She was selected to be a TEDx speaker for 2020.

You can connect with her on her website or on Instagram. 

Check out her book, Building a Healthy Child here. 

Resources:

Check out Daily Harvest for quick and delicious meal options, especially when we’re crazy busy. They’re vegan, gluten-free, and so so good. I love the smoothies, scoops, bowls, and flatbreads! Use the code FITNESSISTA for $25 off your first box.

CBD has changed my life. It helps so much with my anxiety and sense of calmness. You can read more about my experience with CBD here and use the code FITNESSISTA here to get an extra 15% off your first order. (I love the flavored drops!)

Thank you so much for listening and for all of your support with the podcast! Please leave a rating or review if you enjoyed this episode. If you leave a rating, head to this page and you’ll get a little “thank you” gift from me to you.

You can listen and subscribe to the podcast on iTunes, Stitcher, and Google Play.

xoxo

Gina

The post 057: Digestive health and building a healthy immune system with Dr. Melina Roberts appeared first on The Fitnessista.

057: Digestive health and building a healthy immune system with Dr. Melina Roberts published first on https://immigrationways.tumblr.com/

[agritecture]

Nature-inspired water collection system wins $100,000 Ray of Hope Prize®

CONTENT SOURCED FROM BIOMIMICRY INSTITUTE

By 2050, 9 billion people will live on our planet, and 70% of them will live in cities, creating a demand for sustainable local food production solutions. An international team based in New York City has developed a prototype product that mimics the way living systems capture, store, and distribute water, and has been awarded the 2017 $100,000 Ray C. Anderson Foundation Ray of Hope Prize in the Biomimicry Global Design Challenge. 

The challenge is an international design competition and accelerator program that crowdsources nature-inspired climate change solutions. Team NexLoop, whose members include Jacob Russo, Anamarija Frankic, and C. Mike Lindsey, was awarded the prize at the National Bioneers Conference today.

“NexLoop is an impressive team across the board,” said John A. Lanier, executive director of the Ray C. Anderson Foundation. “They have a deep understanding of how biomimicry aids in the design process, and their plans for hyper local water capture and storage in urban settings could play a crucial role in scaling local, sustainable agriculture. We are proud to award them this year’s Ray of Hope Prize.”

Team NexLoop developed the AquaWeb to help urban local food producers collect, filter, store, and distribute atmospheric moisture with a modular, all-in-one water sourcing and management system. AquaWeb harnesses freely available rain and fog and uses passive strategies to distribute this water so that urban farms, including greenhouses, indoor vertical farms, and container farms, can save energy and become more resilient to disturbances.

Each aspect of AquaWeb’s design was inspired by living systems. These include how cribellate orb weaver spider webs collect fog from the air, how drought-tolerant plants like the crystalline ice plant store water, and how mycorrhizal fungi like the Jersey cow mushroom distribute water. The team also looked to the dwarf honey bee’s hexagonal nest structure for AquaWeb’s efficient and modular design.

The trustees of the Ray C. Anderson Foundation also awarded a $20,000 second place prize to Team Windchill from the University of Calgary, Canada, who created an electricity-free refrigeration system inspired by how animals regulate temperature. The $15,000 third place prize went to Team Evolution’s Solutions from the University of California, San Diego, who created a food waste nutrient recycling and supply system inspired by bacteria that helps hydroponic farmers grow food more efficiently and sustainably.

“These teams taught us what is possible when we ask: How does nature preserve? Turn food waste into fertilizer? Allocate nutrients equitably? Pull water from air? Find dispersed nutrients? Cool without refrigeration?” said Janine Benyus, co-founder of the Biomimicry Institute. “Their designs are elegant and refreshingly new approaches to the essential question: How will we feed ourselves in a way that feeds the planet?”

A total of six international teams spent the past year in the world’s only Biomimicry Accelerator program, developing working prototypes with the help of biomimicry experts and business mentors in order to create viable, market-ready solutions. A full list of the finalists’ innovations can be found here. The Biomimicry Accelerator is a commercialization platform for biomimicry entrepreneurs to bring needed sustainability solutions to market faster. The Biomimicry Accelerator is part of the Biomimicry Institute’s Biomimicry Global Design Challenge, a worldwide design competition sponsored by the Ray C. Anderson Foundation that crowdsources biomimetic, or nature-inspired, solutions to climate change issues, like food systems, water management, and alternative energy.

This year marks the second year that the Ray of Hope Prize® was presented at the National Bioneers Conference. The conference, held this year from October 20-22, 2017, is a yearly gathering of dynamic changemakers dedicated to solving our world’s most pressing environmental and social challenges.

“Our vision moving forward is to help seed biomimicry and biomimetic thinking as the default position for design, industry, economy, and culture,” said Kenny Ausubel, Bioneers co-founder and CEO. “The Biomimicry Global Design Challenge doubles down on innovation, providing a business incubation process as well as potential investment capital for the finalists to accelerate market-ready, scalable biomimetic solutions to our greatest challenges. As such, we are honored to be continuing and deepening our partnership with them.”

A new round of the Biomimicry Global Design Challenge has just launched, focused again on finding nature-inspired climate-change solutions. It is a new opportunity for teams to join and compete for the annual $100,000 Ray of Hope Prize. Individuals and teams can learn more about the Challenge at challenge.biomimicry.org.

CONTENT SOURCED FROM BIOMIMICRY INSTITUTE

[seokingstar]

Furnace Installation Calgary

Welcome To Bbbplumbing.ca

Bbbplumbing.ca - The Best Plumbing Services in Calgary!

 Plumbing services Calgary

 Welcome to Best Budget Boiler and Plumbing Inc! Get the best plumbing services in Calgary. We offer the 24-hour water heater repair and furnace repair services in Calgary.

24 hour plumber Calgary

Our general services include:

·         Roughen Plumbing: New Build, Renovation, Basement Development

·         Plumbing Services: Drainage Clogging, Water leak, faucet replacement, Sink replacement

·         Water Heater Services: Tankless Water Heater (Navien), Power Vent Hot Water Tank

·         (Single pipe and two pipes), Atmospheric or standard hot water tank and Indirect water heater

·         Hot tub and Jacuzzi

·         Sump Pump installation

·         Sump and Oil Trap

·         Commercial Kitchen grease trap

·         Garbage Grinder (Garburator)

·         Sub Soil installation all around the house.

 Hydronics

Radiant floor heat

Second-floor joist heating

Baseboard Heating

  Water heater repair Calgary

Water Treatment

Water Softener installation

Water Filtration (For whole house or for kitchen only by RO (Reverses Osmosis), and Carbon filter for whole house

Combo system: Water Softener and Water Filtration combine (North Star City Softener)

 Furnace repair Calgary

At Best Budget Boiler and Plumbing Inc, it provides furnace installation and furnace services in Greater Calgary area. We are direct dealer of Trane and Lennox as our main product.

Trane Furnace

Most Fire Departments, Insurance Companies, and all Furnace Manufacturers recommend you complete an Annual Service & Safety Inspection on your furnace. It’s important to know that Manufacturers are now requiring proof of regular Furnace Servicing to keep your warranty valid. Best Budget Boiler and Furnace Inc. For Furnace installation Calgary is recognized by Furnace Manufacturers for warranty processing. The Annual Furnace Servicing & Safety Inspections will also help keep your heating system in peak operating condition. As part of our 30 point test our Licensed Qualified Gas Technician will also check for any potentially dangerous Gas & Carbon Monoxide leaks in the home. With doing the annual service your  new furnace installation Calgary with Best Budget Boiler and Plumbing Inc.

 WHAT BEST BUDGET BOILER AND PLUMBING INC DOES FOR FURNACE STANDARD SERVICES?

1.      Carbon monoxide (CO) test:  Carbon monoxide is toxic but odorless, tasteless, and colorless. You cant feel it, see it or smell it. If more than 9 particles in millions found in a house, it is a sign of danger. 35 particles your family member will be in real danger to death. Our technician with monoxide detector give you a report what is the stand of your monoxide level. If any monoxide problem found in your house our technician fix it right away for you.

2.      Clocking: clocking means check your whole house for any gas leak. This will be done through your gas meter and double check with your appliances with an engineering calculation by our well trained technicians. Also double check it with gas leak detector.

3.      Dioxide carbon (CO2) test: your heating system should not produce more than 12 % dioxide carbon. The range is between 7% and 12%.  Our technician provides you the report with having your heating system in approved level of dioxide carbon.

4.      For Furnace: Tune up your Furnace, double check your pressure of the furnace gas valve. The normally income pressure should have been 11 IN.WC. and outgoing pressure shall be 3.5 IN.WC. This will be done with a high tech digital barometer Clean the burners, flame rode sensor, and with high pressure pump and vacuum clean your whole system.

5.      For your Boiler: The water in your pipe should not stayed there more than one year, otherwise the water sediment start in the pipe and impacts in the efficiency of the boiler, also lessen the boiler efficiency life. Our Boiler specialist drain the old water of the system, bleed the air from the boiler and lets run the new Double check the pressure of the outgoing water to the house which shall be 20 PSIG, double check of stand of boiler feeding regulator which provide the 20 PSIG to the house piping system, double check the boiler gas valve income and outgoing pressure to the burner. The normally income pressure to the gas valve should have been 11 IN.WC., and outgoing pressure shall be 3.5 IN.WC with a high tech digital barometer.

6.      For Fireplace: Double check the stand of Thermopylae, double check the orifice and pilot. Measure the monoxide and dioxide carbon level, double check for any leaking around the pilot and the burner, clean up the fireplace and double check the stand of flame.

7.      Change the filter, if need it.

8.      Providing an engineering recommendation from BC Best Boiler and Furnace Inc for your heating system to keep your system in standard level to provide you appropriate heat, dangerous free form any the aldehyde (OHC2) and monoxide carbon (CO).

 About Us

We are proud to let you know that we have been a Canadian company for 9 years now. We pride ourselves in providing quality Plumbing, Heating, and Cooling services for a great affordable price. Working within the greater Calgary area, we are a trusted company that many choose to use for their furnace repairs, hot water tank check ups, boiler installations and more. Ever since the beginning, Best Budget Boiler and Plumbing Inc. has only hired skilled technicians to insure quality (Red Seal plumber’s and Red Seal gas fitter’s). Recently we have been providing internships for people; but don’t worry at all as they are accompanied by a master technician.

 Address :- 344 Queensland Rd SE,Calgary, AB T2J 3S6,Alberta,Canada

Phone :- 5874333335

Email :- bbbplumbinginc@gmail.com

 Visit For More Information :- bbbplumbing.ca

[trykangen-blog1]

Best Alkaline Water Machines

If you are looking at alkaline water machines, Calgary residents need to look no farther than your local Enagic distributor, Try Kangen Water. You have probably heard about the many alkaline water benefits and other uses of alkaline ionized water. Best place to start when you want the best alkaline water machines is with the company that pioneered this technology. Go for the Kangen alkaline water machine that best fits your needs, look at the eight made by Enagic. First, we want to look at what to expect from alkalization or ionization of water and then we will consider which of the Kangen water systems is best for you.

What Should You Expect from an Alkaline Water Machine?

An alkaline water machine or ionized water machine electrolyzes water using an electrical current. As you may already know, electrolysis separates water molecules (H2O) into two hydrogen atoms (the H2) and one oxygen atom (the O). During this process, water near one electrode becomes alkaline and water near the other electrode becomes acidic. Thus what alkaline water machines can do is produce either alkaline or acidic water or water that is neutral (neither acidic nor alkaline). When you are looking for a top of the line water ionizer, you should look for an alkaline water machine that can produce strong alkaline water in the pH 11 range, alkaline water in the 8.5 to 9.5 pH range, neutral water with a pH of 7, acidic water with a pH of 4.0 to 6.0 and strongly acidic water with a pH of 2.7. This range of alkalinity to acidity is attainable with the best alkaline water machines from Enagic.

The machine you buy should be able to produce sufficient quantities of strong Kangen water (very alkaline) which you can use for cleaning, disinfecting, and even for softening tough, raw vegetables. Even more importantly, the machine should reliably produce the quantities of alkaline water (Kangen water) that you can use for drinking, making coffee, tea, soups, and more. This is the water that has been recommended for reducing heart burn and acidic reflux damage to the esophagus.

The best alkaline water machines filter and purify your water and deliver perfectly neutral water (pH 7.0) that is ideal for preparing food for the baby.

The mildly acid water produced by a good ionized water machine should be of sufficient quality and in sufficient quantity for use as beauty water for skin and hair care.

And, the best alkaline water machines will produce sufficient amounts of strongly acidic water that can be used for cleaning and disinfecting both at home and in the workplace.

In short, when you are looking for alkaline water benefits and shopping for a machine to produce alkaline water, make sure to look at machines that can produce the full range of alkaline to acidic water that Kangen water machines are capable of.

There is a lot of chemistry to how these machines work. The good part for you is that Kangen water systems have been around for decades, starting in Japan and spreading their benefits across the world. Because Enagic, the folks who bring you the Kangen water Calgary prefers, have done the chemistry and the work, all you need to do is adjust the settings to get the specific water that you wish.

Which Kangen Water Systems Are Right for You?

Enagic offers eight different Kangen water systems. They start with the Leveluk K8 and the Leveluk SD 501, their top of the line machines. There are Enagic Kangen water systems for every home and range of purposes. Let’s take a look at each of these alkaline water machines and what it offers for you.

Leveluk K8

The Kangen 8 is the strongest alkaline water machine that Enagic produces. They refer to it is an antioxidant machine. Its titanium plates are dipped in platinum for the best water ionization and potential for antioxidant production. Enagic sells these through your Enagic distributor (Try Kangen Water) in Calgary. Because these alkaline water machines are sold and used everywhere on the planet, the Leveluk K8 has a multi-voltage power supply and interchangeable plugs are available as well. This great machine is not only powerful. It is user-friendly and comes with a variety of energy-saving features.

The Leveluk K8 produces all five types of alkaline to acidic water which are Strong Kangen Water, Kangen Water, Neutral Water, Beauty Water, and Strong Acidic Water. The extra titanium plate with its platinum coating gives you improved ionization and a sufficient flow rate to use this machine in a small business setting as well as at home.

And, this machine has displays and audio in eight languages! (Japanese, English, French, German, Chinese, Italian, Spanish, Portuguese)

The Leveluk K8 cleans itself and even tells you when it is time to change filters!

Leveluk SD501 Platinum

The Leveluk SD501Platinum is a powerful alkaline water machine that produces all five necessary types of Kangen water. (Strong Kangen Water, Kangen Water, Neutral Water, Beauty Water, Strong Acidic Water) These alkaline water machines are not only incredibly functional but an attractive addition to your kitchen as well. Its seven titanium, platinum-coated plates allow the machine to produce delicious Kangen water at a rate of 1.2 to 2 gallons a minute! The control panel display gives you control of the machine in English, German, French, Italian, or Spanish!

Leveluk SD501

Think of the Leveluk SD501 as the best of the alkaline water machines for home use. Its seven titanium plates provide exceptional electrolysis. The unit is compact so that you can put this fully functional electrolysis alkaline water marker on your kitchen cabinet. This machine tells you when to change filters and tells you in a pleasant voice which water setting you have chosen!

Leveluk Super501

This is the most robust Kangen water system for home use and uses in business and professional settings as well. It has seven and five electrode plates as well as a twin hose system. The electrolysis enhancer has a built-in take and the unit has a water pressure regulator that lets it adapt to the high level of use seen with a large family or in a professional or business setting.

The Leveluk Super501 can generate any of the five different types of Kangen water at two gallons a minute for thirty minutes and then recycle and do it again.

Leveluk JRII

Think of this unit as the junior edition of the more powerful units. This can be used as a “starter” model or simply all that you need for a small household. The JRIII makes all five types of Kangen water. Because it has 3 electrolysis plates, it uses less power. But, it works just a smoothly as the larger models, tells you when to change filters, and cleans itself automatically.

Leveluk R

This “starter” model in the series is very affordable, has fewer power requirements with its three titanium plates, and is just as easy to operate as its larger brothers. This unit produces the three “middle” ionized water types, Kangen water, neutral water, and beauty water.

[savetopnow]

2018-03-28 20 PHOTO now

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