Renewable Energy Systems Analysis
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Investigation of the Impact of Commercial Building Envelope Airtightness on HVAC Energy Use
NISTIR 7238 Investigation of the Impact of Commercial Building Envelope Airtightness on HVAC Energy Use Steven J. Emmerich Tim McDowell Wagdy Anis NISTIR 7238 Investigation of the Impact of Commercial Building Envelope Airtightness on HVAC Energy Use Steven J. Emmerich Building and Fire Research Laboratory Timothy P. McDowell TESS, Inc. Wagdy Anis Shepley Bulfinch Richardson and Abbott Prepared for: U.S. Department of Energy Office of Building Technologies June 2005 U.S. Department of Commerce Carlos M. Gutierrez, Secretary Technology Administration Phillip J. Bond, Under Secretary of Commerce for Technology National Institute of Standards and Technology Hratch Semerjian, Acting Director ABSTRACT This report presents a simulation study of the energy impact of improving envelope airtightness in U.S. commercial buildings. Despite common assumptions, measurements have shown that typical U.S. commercial buildings are not particularly airtight. Past simulation studies have shown that commercial building envelope leakage can result in significant heating and cooling loads. To evaluate the potential energy savings of an effective air barrier requirement, annual energy simulations were prepared for three nonresidential buildings (a two-story office building, a one-story retail building, and a four-story apartment building) in 5 U.S. cities. A coupled multizone airflow and building energy simulation tool was used to predict the energy use for the buildings at a target tightness level relative to a baseline level based on measurements in existing buildings. Based on assumed blended national average heating and cooling energy prices, predicted potential annual heating and cooling energy cost savings ranged from 3 % to 36 % with the smallest savings occurring in the cooling-dominated climates of Phoenix and Miami. -
Infiltration Modeling Guidelines for Commercial Building Energy Analysis
PNNL-18898 Prepared for the U.S. Department of Energy under Contract DE-AC05-76RL01830 DOCKET 12-BSTD-1 DATE RECD. MAY 15 2012 Infiltration Modeling Guidelines for Commercial Building Energy Analysis K Gowri D Winiarski R Jarnagin September 2009 ii Executive Summary This report presents a methodology for modeling air infiltration in EnergyPlus to account for envelope air barrier characteristics. Based on a review of various infiltration modeling options available in EnergyPlus and sensitivity analysis, the linear wind velocity coefficient based on DOE-2 infiltration model is recommended. The methodology described in this report can be used to calculate the EnergyPlus infiltration input for any given building level infiltration rate specified at known pressure difference. The sensitivity analysis shows that EnergyPlus calculates the wind speed based on zone altitude, and the linear wind velocity coefficient represents the variation in infiltration heat loss consistent with building location and weather data. EnergyPlus infiltration input is calculated to be 0.2016 cfm/sf of exterior wall area, assuming that uncontrolled air leakage through the building envelope can be specified by a baseline leakage rate of 1.8 cfm/sf (@ 0.30 in. w.c) of exterior above grade envelope area (based on ASHRAE SSPC-90.1 Envelope Subcommittee recommendation). iii Contents 1. Introduction ................................................................................................................................ 4 2. Building Infiltration Rate ........................................................................................................... -
Home Fires Involving Heating Equipment
Home Fires Involving Heating Equipment December 2018 Richard Campbell ©December 2018 National Fire Protection Association Key Findings Local fire departments responded to an estimated average of 52,050 fires involving heating equipment each year in 2012-2016. Home fires involving heating equipment caused an estimated average of 490 civilian deaths and 1,400 civilian injuries each year in 2012-2016, as well as an estimated $1.03 billion in direct property damage a year. Space heaters accounted for more than two in five (44%) of home heating equipment fires, but these fires were responsible for 86% of civilian deaths and 78% of civilian injuries caused by heating fires. Fires in which the heat source was too close to combustibles were associated with the largest shares of civilian deaths, civilian injuries, and direct property damage. Home heating equipment fires are less likely to occur in the overnight hours between midnight and 8 a.m. (19% of total), but these fires account for almost half (48%) of the civilian deaths. Nearly half (48%) of all home heating fires occurred in December, January, and February. Home Fires Involving Heating Equipment Heating equipment is a leading cause of fires in U.S. One dies, three injured when fireplace ember starts homes. Heating equipment was responsible for 15% of house fire home structure fires in 2012-2016, ranking as the second leading cause behind fires caused by cooking A 60-year-old man died and three female residents were injured in an early morning house fire that started equipment. Home heating equipment fires also when wind blew a fireplace ember onto a nearby sofa accounted for nearly one-fifth (19%) of civilian deaths and the resulting fire rapidly spread, cutting off escape (tied for third behind fires caused by smoking materials through the front door. -
Heat Pump Technology Opportunities in Santa Clara County a COST-EFFECTIVENESS STUDY
Heat Pump Technology Opportunities in Santa Clara County A COST-EFFECTIVENESS STUDY April 2019 ` Heat Pump Technology Opportunities in Santa Clara County Executive Summary Nearly one third of Silicon Valley Clean Energy’s (SVCE’s) greenhouse gas (GHG) emissions are from the combustion of natural gas in building appliances, such as for space and water heating. Given SVCE’s carbon-free electricity supply, a key strategy to reduce GHG emissions from the built environment is to replace natural gas appliances with efficient electric appliances that run on clean electricity. This fuel-switching activity is referred to as “electrification.” This report documents a cost-effectiveness analysis of space conditioning and water heating electrification opportunities in Santa Clara County, the two end uses which are responsible for the majority of natural gas consumption in buildings. The lifetime net cost of ownership was calculated and compared for natural gas and electric appliances, for water heating, space heating and combined space heating and cooling, for both single-family residential and small commercial buildings. The cost-effectiveness evaluation was carried out from the customer perspective, meaning all costs and revenues born by the customer were considered, including, for instance, installation costs, equipment costs, and ongoing fuel costs. Electrifying an end use is cost-effective if the lifetime net cost of ownership for the electric appliance is lower than that of the natural gas appliance. The costs were also expressed in terms of the incremental cost of GHG abatement, to facilitate comparisons to other GHG abatement measures. The sensitivity of the results to the various input assumptions was captured through a scenario analysis and represented as error bars in the figures of results. -
A Consumer's Guide: Heat Your Water with the Sun (Brochure)
A Consumer’s Guide Heat Your WaterwiththeSun Bringing you a prosperous future where energy is clean, abundant, reliable, and affordable Contents Background What is solar heating? . 2 What are the basic components of a solar thermal system? . 2 How have solar systems improved? . 5 Investing in solar thermal technologies Why should I invest in a solar thermal system? . 6 How much will your solar heating system help the environment? . .6 Is my home a good place for a solar heating system? . 6 How big should my solar thermal system be, and which features should I look for? . 7 How much money will my solar thermal system save, and how much will it cost? . 9 How can I finance the cost of my solar thermal system? Are there incentives? . 11 What are the maintenance issues and repair costs for a solar thermal system? . 12 Selecting a solar heating contractor Who sells and installs solar thermal systems? . 13 How do I choose among solar thermal system providers? . 13 How do I choose among bids? Is the least expensive the best deal? . 14 Before you put solar heating to work Do I need a conventional system as a backup? . 15 Will I need any permits or inspections? . 16 What about insurance? . 16 Will I need warranties? . 16 Will I need a maintenance agreement? . 16 Getting help . 17 Cover photo: The people living in this house enjoy hot water that is heated with a solar thermal system. (Courtesy of Industrial Solar Technology/PIX12964) Photo opposite: Flat-plate solar collectors heat this pool in Oregon. -
Indoor Air Quality (IAQ): Combustion By-Products
Number 65c June 2018 Indoor Air Quality: Combustion By-products What are combustion by-products? monoxide exposure can cause loss of Combustion (burning) by-products are gases consciousness and death. and small particles. They are created by incompletely burned fuels such as oil, gas, Nitrogen dioxide (NO2) can irritate your kerosene, wood, coal and propane. eyes, nose, throat and lungs. You may have shortness of breath. If you have a respiratory The type and amount of combustion by- illness, you may be at higher risk of product produced depends on the type of fuel experiencing health effects from nitrogen and the combustion appliance. How well the dioxide exposure. appliance is designed, built, installed and maintained affects the by-products it creates. Particulate matter (PM) forms when Some appliances receive certification materials burn. Tiny airborne particles can depending on how clean burning they are. The irritate your eyes, nose and throat. They can Canadian Standards Association (CSA) and also lodge in the lungs, causing irritation or the Environmental Protection Agency (EPA) damage to lung tissue. Inflammation due to certify wood stoves and other appliances. particulate matter exposure may cause heart problems. Some combustion particles may Examples of combustion by-products include: contain cancer-causing substances. particulate matter, carbon monoxide, nitrogen dioxide, carbon dioxide, sulphur dioxide, Carbon dioxide (CO2) occurs naturally in the water vapor and hydrocarbons. air. Human health effects such as headaches, dizziness and fatigue can occur at high levels Where do combustion by-products come but rarely occur in homes. Carbon dioxide from? levels are sometimes measured to find out if enough fresh air gets into a room or building. -
Modeling of Airflow Infiltration Through Building Entrance Doors
Validation of Numerical Modeling of Air Infiltration through Building Entrance Doors Sherif Goubran, Dahai Qi, Wael F. Saleh, Liangzhu (Leon) Wang, Radu Zmeureanu Department of Building, Civil and Environmental Engineering, Concordia University, Quebec, Canada ABSTRACT studies confirm that with the increase of efficiency of equipment and building envelope, the relative percent Air infiltration through building entrance doors has energy loss due to air infiltration is becoming more been the focus of many studies due to the significant significant (in relation to the total energy losses) effect infiltrated air has on the buildings’ energy (Deru, Field, Studer, & Benne, 2011; Ng, Emmerich, performance. Air infiltration models were developed & Persily, 2014). Thus in modern and well insulated for the double swing single and vestibule doors based commercial buildings a larger portion of the heat on previous studies. It was concluded that vestibules losses are contributed to air infiltration; air infiltration doors are effective in reducing air infiltration. is responsible for about 25% of the building heating Currently vestibules are required as an energy saving loads for new buildings (Emmerich & Persily, 1998). measure for most commercial buildings. Our recent With tight building envelopes, the major sources of air studies were focused on investigating the effectiveness infiltration that remain in buildings are the exterior of different entrance doors in reducing air infiltration openings (doors and windows) (Cho, Liu, & Gowri, in buildings. This paper presents the results from a 2010; Emmerich & Persily, 1998; Ng et al., 2014). preliminary effort in our recent studies: the experimental validation of the numerical modeling of Yuill conducted one of the pioneer studies on a 2.44 m air infiltration through single doors (double swing) × 2.44 m × 1.30 m (L × W × H) chamber to estimate using computational fluid dynamics (CFD). -
Influence of Air Infiltration on Combustion Process Changes in A
processes Article Influence of Air Infiltration on Combustion Process Changes in a Rotary Tilting Furnace Róbert Dzur ˇnák 1,* , Augustin Varga 1, Gustáv Jablonský 1 , Miroslav Variny 2 ,Réne Atyafi 1, Ladislav Lukáˇc 1 , Marcel Pástor 1 and Ján Kizek 3 1 Department of Thermal Technology and Gas Industry, Institute of Metallurgy, Faculty of Materials, Metallurgy and Recycling, Technical University of Kosice, Letna 9, 042 00 Kosice, Slovakia; [email protected] (A.V.); [email protected] (G.J.); rene.atyafi@tuke.sk (R.A.); [email protected] (L.L.); [email protected] (M.P.) 2 Department of Chemical and Biochemical Engineering, Faculty of Chemical and Food Technology, Slovak University of Technology in Bratislava, Radlinskeho 9, 812 37 Bratislava, Slovakia; [email protected] 3 Department of Process Technique, Faculty of Manufacturing Technologies of the TU of Kosice with a Seat in Presov, Technical University of Kosice, Sturova 31, 080 01 Presov, Slovakia; [email protected] * Correspondence: [email protected] Received: 24 September 2020; Accepted: 13 October 2020; Published: 15 October 2020 Abstract: Air infiltration into the combustion chambers of industrial furnaces is an unwanted phenomenon causing loss of thermal efficiency, fuel consumption increase, and the subsequent increase in operating costs. In this study, a novel design for a rotary tilting furnace door with improved construction features is proposed and tested experimentally in a laboratory-scale furnace, aimed at air infiltration rate reduction by decreasing the gap width between the static furnace door and the rotating body. Temperatures in the combustion chamber and oxygen content in the dry flue gas were measured to document changes in the combustion process with the varying gap width. -
Electric Space Heater FILE #E21609 Installation & Maintenance Instructions
UH Series Electric Space Heater FILE #E21609 Installation & Maintenance Instructions SPECIFICATIONS: UH724ST Mounting Height, ft. (mm) Heater Rating and Voltage BTU per Phase Contactor Horizontal Air Min. Distance from Hr. Built-in Vertical Installation Horizontal Installation Throw, ft. (mm) Mounting Hole to BTUH Min. Max. Min. Max. Wall, in (mm) •7500 W @ 240V 25,598 6250W @ 240V 21,331 1 Yes 6' 11' 6' 8' 18' ••13" 5000W @ 240V 17,065 (1829) (3353) (1829) (2439) (5486) (330) 3750W @ 240V 12,799 •5625W @ 208V 19,198 4685W @ 208V 15,990 6' 11' 6' 8' 18' ••13" 3750W @ 208V 12,799 1 Yes (1829) (3353) (1829) (2439) (5486) (330) 2812W @ 208V 9,598 • Heater is shipped from factory wired for these wattages. Heater can be field adjusted to the other wattages. Refer to “Adjusting the Heat Output” on page 4. •• 48" (1219mm) when heater air flow is between 45° downward and vertical. ! WARNING Read Carefully - These instructions are written to help you prevent the heater must be grounded as a precaution against possible difficulties that might arise during installation of heaters. Studying the electrical shock. Heater circuit must be protected with proper instructions first may save you considerable time and money later. fuses. See Table 1 on page 4. Observe the following procedures, and cut your installation time to a 5. The mounting structure and the anchoring hardware must be minimum. TO REDUCE RISK OF FIRE OR ELECTRIC SHOCK: capable of reliably supporting the weight of the heater and, if 1. Use minimum 60° copper wire only. used, the mounting bracket. 2. -
Factors Affecting Indoor Air Quality
Factors Affecting Indoor Air Quality The indoor environment in any building the categories that follow. The examples is a result of the interaction between the given for each category are not intended to site, climate, building system (original be a complete list. 2 design and later modifications in the Sources Outside Building structure and mechanical systems), con- struction techniques, contaminant sources Contaminated outdoor air (building materials and furnishings, n pollen, dust, fungal spores moisture, processes and activities within the n industrial pollutants building, and outdoor sources), and n general vehicle exhaust building occupants. Emissions from nearby sources The following four elements are involved n exhaust from vehicles on nearby roads Four elements— in the development of indoor air quality or in parking lots, or garages sources, the HVAC n loading docks problems: system, pollutant n odors from dumpsters Source: there is a source of contamination pathways, and or discomfort indoors, outdoors, or within n re-entrained (drawn back into the occupants—are the mechanical systems of the building. building) exhaust from the building itself or from neighboring buildings involved in the HVAC: the HVAC system is not able to n unsanitary debris near the outdoor air development of IAQ control existing air contaminants and ensure intake thermal comfort (temperature and humidity problems. conditions that are comfortable for most Soil gas occupants). n radon n leakage from underground fuel tanks Pathways: one or more pollutant pathways n contaminants from previous uses of the connect the pollutant source to the occu- site (e.g., landfills) pants and a driving force exists to move n pesticides pollutants along the pathway(s). -
Ventilation Heat Recovery Ventilation Glazing; Equipment Insulation
Town of Warner Building Energy Performance Reports Social Services Government Roads Police Fire Waste Material Waste Water Garage 1 2008 Town Building Energy Use 2 4 5 Oil: 4567 gallons Oil: 4057 gallons LP: 5,122 gallons Elec: 20,160KWH Elec: 19,428KWH Elec: 21,120KWH 72KBtu/ft2 57.4KBtu/ft2 48.4KBtu/ft2 3 8 6* LP: 2,033 gallons Oil: 817 gallons Kerosene: 934 gallons Elec: 19,750KWH Elec: 7,290KWH Elec: 18,731KWH 59.6KBtu/ft2 29.4KBtu ft2 45KBtu/ft2 1 Gallons Btu’s Dollars 7 Oil 10,706 1,483MM $32,118 LP: 2200 gallons LP 9,455 861MM $11,555 Oil: 152 gallons Elec: 130,968KWH Elec 237,906 812MM $37,332 Elec: 459KWH *289KBtu/ft2 TOTALS 2,946MM $81,000 33.8KBtu/ft2 2 Town Building 2008 Utility Costs 3 4 2 $17,615 $15,413 $19,081 5 7 6 $7,005 $9,217 $3,869 8 1 $24,500 $658 3 Town Building 2008 Greenhouse Emissions 2 3 4 120,054lbs 104,184lbs 78,508lbs 5 7 6 34,109lbs 39,232lbs 23,379lbs 8 1 121,507lbs 3,712lbs 4 Town Building Air Leakage Rates 6ACH50 8ACH50 .79cfm/ft2shell 1.21cfm/ft2shell Not tested 2 16ACH50 9ACH50 Not tested 1.3cfm/ft2shell .99cfm/ft2shell ACH50 – Air changes per hour at - 50Pa; relative to building volume 1 6ACH50 33 ACH50 .45cfm/ft2shell Cfm/ft2 shell – cubic feet of air per minute relative to surface area of shell 2.22cfm/ft2shell 5 Summary of Prominent De-ficiencies Insulation Heat Recovery Insulation Ventilation Heat Recovery Ventilation Glazing; Equipment insulation Air Sealing Air Sealing Air Sealing Insulation insulation Equipment Insulation Air Sealing Electric Loads glazing AS / HRV insulation 6 Prioritize by -
Use of Ductless Mini Split Electric Heat Pumps In
/i U.S. Department of Houslng and Urtan Development lr Office of Policy Development and Researcf USE OF DUCTLESS MINI.SPLIT ELECTRIC HEAT PUMPS IN RESIDENCES Phase ll - Final Report -i U.S. Department of Houslng and Urban Development 1r office of Policy Development and Researci USE OF DUCTLESS MINI.SPLIT ELECTRIC HEAT PUMPS IN RESIDENCES Phase ll - Final Report USE OF DUCTLESS MINI.SPLIT ELEGTRIC HEAT PUMPS IN RESIDENCES Phase ll - Final Report Prepared for: U.S. Department of Housing and Urban Development Office of Policy Development and Research Prepared by: NAHB Research Center Upper Marlboro, MD lnstrument No. DUl 00K000005897 July 1994 Notice The U.S. Govemment does not endorse products or manufacturers. Trade or manufacturers' names aPPear herein solely because they are considered essential to the object of this report. The contens of this rcport are the views of the contractor and do not necessarily rcflect the views or policies of the U.S. Departnent of Housing and Urban Development or the U.S. Govemment. Acknowledgements This report was prepared by the NAHB Research Center through funding provided by the U.S. Department of Housing and Urban Development (HUD). The principal author was C. Edward Barbour with technical assistance and review provided by Mark Nowak and Tom Kenney. Data acquisition system installation and operation was provided by Jay Crandell and J. Alben van Overeem. The author acknowledges the contributions and guidance of Mark Gibson and Carol Soble at various times during the project and development of the report. Special appreciation is extended to William Freeborne of HUD for review assistance.