22-Mec-B2 Environmental Control in Buildings · December 2019
Question 6 of 8: Degree-day estimate for a Winnipeg building — gas quantity, relative cost and primary energy
Nivaar worked solution (AI-drafted; not reviewed by a licensed engineer)
Notes on this paper
Paper format. National Examinations, December 2019 — 16-Mec-B2 Environmental
Control in Buildings. Three hours, open book: only textbooks and reference books are permitted
(no notes and no solved problems), any non-communicating calculator is allowed, and candidates are
expected to bring both an environmental-control text and steam tables because the tables and graphs
in those books are needed. Eight problems are printed at 20 points each and only the first
five in the exam book are graded, so the printed paper totals 160 points and a graded script
totals 100. Psychrometric charts (IP and SI) and an R-134a pressure–enthalpy diagram are
attached as the last three pages. All eight problems are worked below.
McQuiston, Parker & Spitler, Heating, Ventilating and Air Conditioning: Analysis and
Design, 6th ed. — plant psychrometry, duct design, infiltration and the degree-day method.
Jones, Air Conditioning Engineering, 5th ed. — percentage saturation, cooling-tower
analysis, apparatus dew point and coil by-pass factor.
Çengel & Ghajar, Heat and Mass Transfer, 6th ed., Ch. 3 —
one-dimensional composite walls and thermal bridging; Table A-5 for building-material
conductivities.
Stoecker & Jones, Refrigeration and Air Conditioning, 2nd ed. — vapour-compression
cycles and heat pumps; ASHRAE Refrigerant Tables for R-134a on the datum of the attached
chart (hf = sf = 0 at −40 °F).
Eastop & McConkey, Applied Thermodynamics for Engineering Technologists, 5th ed.
— the SI cooling-tower mass/energy balance in the form this paper uses.
Canadian context: ASHRAE Standard 170 Ventilation of Health Care
Facilities (adopted by CSA Z317.2 for Canadian hospitals); Health Canada
Residential Indoor Air Quality Guidelines; National Building Code of Canada 9.36 and the
National Energy Code of Canada for Buildings (NECB 2020); Environment and Climate Change Canada
Canadian Climate Normals for degree-day and design-temperature data.
Check — assumptions declared under cover-page instruction 1
Cover-page instruction 1 asks candidates to state any interpretive assumption with the answer.
Four are needed on this paper and each is flagged again where it is used: the operating-room
dry-bulb temperature in Problem 1 (not given — taken as
75 °F, the top of the ASHRAE 170 range, because it is the
only part of that range that also satisfies the 60 % relative-humidity ceiling); the
Winnipeg design conditions and degree-day base in Problem 6 (the paper says
“select the design conditions”); the indoor design temperature and neutral pressure
level in Problem 7(b); and the duct roughness and fitting allowance in
Problem 8. Everything else in the paper is fully determined by the data given.
Question 6: Degree-day estimate for a Winnipeg building — gas quantity, relative cost and
primary energy (20 marks)
Selected design conditions (the paper says “select the design conditions”)
Winnipeg 99.6 % heating dry bulb
to,design
−33 °C
Indoor design temperature
ti
21 °C
Heating degree-days, base 18 °C (Winnipeg A)
HDD18
5 670 °C·day
Degree-day correction factor
CD
0.70
Find. The annual natural-gas volume, the equivalent electrical energy at
100 % efficiency, the ratio of annual heating costs, the primary-energy comparison between a gas
furnace and an electric furnace, and a comment on the environmental consequences.
Approach. Convert the design load and the selected climate into equivalent
full-load hours by the modified degree-day method, multiply out the annual delivered heat, then divide
by each conversion chain in turn — furnace efficiency for gas, unity for electric resistance, and
generating-plus-transmission efficiency for the primary-energy comparison.
Select and justify the design conditions. Environment and Climate Change Canada's
1981–2010 normals give Winnipeg Richardson International Airport
HDD18 = 5 670 °C·day, and the ASHRAE
99.6 % heating dry bulb for the same station is about −33 °C. With a
21 °C indoor design temperature the design temperature difference is
$$\Delta T_{design} = 21 - (-33) = 54\ \text{K}$$
Winnipeg is one of the coldest major cities in Canada, and both figures matter: the design temperature
difference sets how hard the plant works at its worst hour, and the degree-days set how long it works
over the year.
Convert the design load and climate into equivalent full-load hours. The modified
degree-day method writes the annual heating requirement as the design load multiplied by the hours the
plant would have to run at full output to deliver it:
$$\text{EFLH} = \frac{24\,\text{HDD}\,C_D}{\Delta T_{design}}
= \frac{24 \times 5\,670 \times 0.70}{54} = \boxed{1\,764\ \text{h}}$$
The correction factor CD ≈ 0.70 accounts for internal and
solar gains, off-cycle losses and the fact that the base-18 °C convention is only an
approximation to the building's true balance point. Between 2 000 and 2 500 full-load hours is
typical for southern Ontario; 1 764 h for the colder but sunnier and drier Prairies is a
sensible figure.
The natural-gas quantity. Dividing by the furnace efficiency and the heating value,
$$V_{gas} = \frac{Q_{annual}}{\eta_f \times HV}
= \frac{635\,040\ \text{MJ}}{0.85 \times 37\ \text{MJ/m}^3}
= \frac{635\,040}{31.45} = \boxed{20\,190\ \text{m}^3\!/\text{yr}}$$
which is about 747 GJ of gas purchased to deliver 635 GJ of heat.
The electrical alternative at 100 % efficiency. A resistance furnace converts
every kilowatt-hour at the meter into a kilowatt-hour of heat in the building, so
$$E_{elec} = \frac{Q_{annual}}{\eta_e} = \boxed{176\,400\ \text{kWh/yr}}$$
Compare the annual costs.
$$\text{Cost}_{elec} = 176\,400 \times 0.10 = \boxed{17\,640\ \text{\$/yr}}$$
$$\text{Cost}_{gas} = 20\,190 \times 0.1175 = \boxed{2\,373\ \text{\$/yr}}$$
so electric resistance heating costs 7.4 times as much. Put on a common basis,
gas delivers heat at 1.35 ¢/kWh against electricity's 10.0 ¢/kWh — a gap so
large that no plausible variation in the degree-day estimate closes it, because the ratio depends only
on the two prices, the heating value and the furnace efficiency, not on the annual quantity at
all.
Compare on primary energy, which is what the 33 % is for. The exam supplies
the generating efficiency precisely so that the two options can be referred to the same boundary
— fuel at the mine or the wellhead, rather than energy at the building's meter:
$$PE_{gas} = \frac{Q_{annual}}{\eta_f} = \frac{635\,040}{0.85} = 747\,100\ \text{MJ}$$
$$PE_{elec} = \frac{Q_{annual}}{\eta_{plant}\,\eta_{td}} = \frac{635\,040}{0.33 \times 0.93}
= 2\,069\,000\ \text{MJ}$$
including a 7 % allowance for transmission and distribution losses. The electric furnace therefore
consumes
$$\frac{PE_{elec}}{PE_{gas}} = \boxed{2.8\ \text{times}}$$
the primary energy of the gas furnace — 2.6 times if transmission losses are ignored. The
same arithmetic gives the threshold at which an electrically driven machine would break even with the
gas furnace on primary energy:
COP = ηf/(ηplantηtd) = 2.77. A
resistance furnace at COP 1.00 fails that test by a wide margin; a heat pump at COP 3.5 passes
it comfortably, which is the real conclusion buried in this part of the question.
Comment on the environmental consequences — and on why the 33 % plant is the
wrong plant for Winnipeg. Burning 20 190 m³ of natural gas at
1.888 kg CO₂/m³ emits 38 tonnes of CO₂ a year. If the
electricity really came from the 33 %-efficient thermal plant the question posits — a
coal-fired station at roughly 1.0 kg CO₂e/kWh — the electric furnace would emit
about 180 tonnes, nearly five times as much, so on that grid the primary-energy
answer and the carbon answer point the same way. But the building is in Manitoba, whose grid
is over 97 % hydroelectric at an emission factor near
1.2 g CO₂e/kWh, and the same 176 400 kWh would emit about
0.2 tonnes — roughly 180 times less than the gas furnace. The
lesson is that primary-energy accounting and carbon accounting are different questions with different
answers, and that an electric heating technology is exactly as clean as the generation behind it.
Three consequences follow for a real Winnipeg design: gas remains far cheaper to run, so an
operating-cost argument favours it; carbon pricing and Canada's Clean Electricity
Regulations steadily erode that advantage; and the design that satisfies both criteria is neither
of the two the question offers, but a ground-source heat pump on the Manitoba grid, which would cut the
primary energy below the gas furnace's and the emissions to near zero.
Check — sensitivity of the gas estimate
The degree-day answer is only as good as its two selected inputs. Holding everything else fixed,
CD = 0.60 gives 17 310 m³/yr and
CD = 0.80 gives 23 080 m³/yr, while using the
Winnipeg city-station HDD18 = 5 777 instead of the airport
value moves the answer to 20 570 m³/yr. The estimate should therefore be reported as
roughly 20 000 m³ with a ±15 % band, not as five significant figures. Note
that none of the cost or primary-energy ratios in steps 6 and 7 depends on these
inputs.
Quantity
Symbol
Result
Design temperature difference
ΔTdesign
54 K (21 °C indoor, −33 °C design)
Equivalent full-load hours
EFLH
1 764 h
Annual delivered heat
Qannual
176 400 kWh (635 GJ)
Natural gas required
Vgas
20 190 m³/yr (±15 %)
Electrical energy at 100 %
Eelec
176 400 kWh/yr
Annual cost: gas / electricity
—
$2 373 / $17 640
Relative heating cost
—
electricity 7.4 × gas (10.0 vs 1.35 ¢/kWh delivered)