In this lesson, we'll go over solar and anaerobic digestion in a little more detail. We will see some of this in our travels, and I want you to have a better understanding of some of the basics.
By the end of this lesson, you should be able to:
To Read | Lesson 6 Online Content | You're here! |
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To Do |
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If you have any general course questions, please post them to our HAVE A QUESTION discussion forum located under the Discussions tab in Canvas. I will check that discussion forum regularly to respond as appropriate. While you are there, feel free to post your own responses and comments if you are able to help out a classmate. If you have a question but would like to remain anonymous to the other students, email me through Canvas.
If you have something related to the material that you'd like to share, feel free to post to the Coffee Shop forum, also under the Discussions tab in Canvas.
As was detailed in an earlier lesson, solar energy is electromagnetic (aka radiant) energy that is generated by the (nuclear) fusion of hydrogen atoms into helium atoms in the sun. The amount of radiant energy that is released by an object is related to its temperature, and since the sun is so hot (~10,000º F!) [1], it is able to reach the ~94,000,000 miles (the distance depends on the time of year) to the earth. It is a massive amount of energy! A commonly cited statistic is that enough solar energy reaches the earth each hour to provide all of humanity's energy for an entire year. There is no shortage of solar energy.
Without the sun, life on earth would not be possible. It provides energy for vegetation to grow and provides sufficient heat to allow water to exist in liquid form, among other things. But there are many ways that humans can use this radiant energy more deliberately. The following is an overview of the major types of solar technologies. We could spend weeks analyzing each of these - keep in mind that this is just an overview.
The rest of the solar lesson will focus on solar photovoltaics or solar PV. As noted above, photovoltaic technology (aka the photovoltaic effect) converts radiant solar energy into electricity. View the short video below from the U.S. Department of Energy for a brief explanation. Note that the narrator of the video indicates that photons provide the energy that is converted into electricity. NASA describes [4] the relationship between photons and electromagnetic energy thusly: "Electromagnetic radiation can be described in terms of a stream of mass-less particles, called photons [5], each traveling in a wave-like pattern at the speed of light [6]." So photons are generally considered to be what carries the energy that is emitted in waves.
Okay, so a solar panel converts radiant to electrical energy by using the unique properties of a semiconductor, usually, silicon combined (doped) with other elements (usually boron and phosphorous). But how much energy and power does a panel generate? As you might guess, it depends on a lot of factors. The following is an overview of some of these factors.
We will experience some solar PV installations and technology while traveling, so I provide some more details about it below.
A few more terms that are important to know:
Recall that the rule of thumb is that the optimal tilt is "latitude tilt," and the ideal orientation in the Northern Hemisphere is due south (180º). This begs the question: what happens if the tilt and orientation are not optimal? The answer, as you might guess, is "it depends." This impact can be quantified by something that is called tilt and orientation factor (TOF). The tilt and orientation factor is a decimal that indicates what percent of the maximum solar output you would receive throughout the year at said tilt and orientation. So if you install an array and it has a TOF of 0.85, that means that it will only be able to output about 85% of the energy it would output if it were at the ideal tilt and orientation.
Wilmington, Delaware is at about 40º north. As it turns out, the ideal tilt is closer to 35º (rules of thumb are only rules of thumb, after all!). The tables below show the TOF at different tilts and azimuths. The first table illustrates the TOFs of different tilts, all with an orientation of 180º. The second table shows the TOFs at different azimuths, all at a tilt of 35º (the ideal tilt).
Tilt (º) | Azimuth (º) | TOF |
---|---|---|
0 | 180 | 0.87 |
5 | 180 | 0.905 |
10 | 180 | 0.935 |
15 | 180 | 0.959 |
20 | 180 | 0.978 |
25 | 180 | 0.991 |
30 | 180 | 0.999 |
35 | 180 | 1.0 |
40 | 180 | 0.996 |
45 | 180 | 0.985 |
50 | 180 | 0.969 |
55 | 180 | 0.947 |
60 | 180 | 0.92 |
65 | 180 | 0.888 |
70 | 180 | 0.851 |
75 | 180 | 0.81 |
80 | 180 | 0.764 |
85 | 180 | 0.715 |
90 | 180 | 0.662 |
Tilt (º) | Azimuth (º) | TOF |
---|---|---|
35 | 90 | 0.797 |
35 | 100 | 0.833 |
35 | 110 | 0.897 |
35 | 120 | 0.898 |
35 | 130 | 0.926 |
35 | 140 | 0.951 |
35 | 150 | 0.972 |
35 | 160 | 0.986 |
35 | 170 | 0.996 |
35 | 180 | 1.0 |
35 | 190 | 0.997 |
35 | 200 | 0.989 |
35 | 210 | 0.976 |
35 | 220 | 0.956 |
35 | 230 | 0.932 |
35 | 240 | 0.905 |
35 | 250 | 0.874 |
35 | 260 | 0.839 |
35 | 270 | 0.803 |
Okay, now we're ready to calculate the solar output. There are a number of software programs and a formula or two that can do this, but the National Renewable Energy Laboratory (NREL) provides a free one that is well-regarded in the energy industry called PVWatts [12]. In the video below, I demonstrate how to calculate the annual output of the array in the images above, which has the following specs:
Hopefully, by now you have a relatively good grasp on some of the considerations that go into designing and calculating the output of solar PV. Solar PV really took off in the early- to mid-2000s, led by residential array installations, which generally had capacities of a few kW. The solar industry in the U.S. is now dominated by utility-scale solar, which is much cheaper per W to construct because of economies of scale. Utility-scale arrays can be thousands of watts (multiple MWs) in capacity!
There are a few ways that people can use and pay for solar PV:
Incentives have played a very important role in the growth of the solar industry, and renewable energy in general. The following provides a description of some incentives.
States and countries have implemented a variety of policies meant to incentivize or encourage private investment in clean, renewable energies. The most common of these policies are tax credits, grants/rebates, and performance-based incentives (PBI), including feed-in tariffs (FIT) and renewable portfolio standards (RPS).
A tax credit is just that, a credit. When an individual or business investor earns a tax credit it means that the amount of the credit will be subtracted from a future tax bill. For example, in the United States, we have a Federal Residential Renewable Energy Tax Credit [15] available to the residential (not commercial or industrial) sector which provides a tax credit covering 26% of the cost of an installation. A typical residential system costs about $3/Watt to install. If you put a 7 kW photovoltaic system on your roof, it should cost around $21,000 before incentives (7,000 W x $3/W). If so, you would earn a $5,460 tax credit. The government doesn’t mail you a check for this amount. It means you get to deduct that amount from your next tax payment. To realize this money, you will need to have paid at least $5,460 in taxes, but excess credits can "generally" be carried over to future tax years. Note that even if you were owed a refund, this tax credit can be used to increase your refund, as long as you paid at least $5,460 in federal income tax throughout the year. Other renewable energy technologies qualify for this credit. See the link above for details.
A rebate means that a government agency or other group (sometimes utility companies) will refund some of the investment. These are usually based on the size/capacity of the system. For example, Pennsylvania used to provide a solar rebate program that provided rebates to investors of $1.75/Watt. Rebates are checks mailed directly to the investor (or their designate). Many states still have such programs such this solar PV rebate program in Oregon [16](description from DSIRE of course!). Different states often have different program specifics. See DSIRE for more examples of programs. Specifics vary within states as well. The program in Oregon, for example, has different rebate levels for different utilities and for different sectors (residential, agricultural, industrial, non-profit, government). For example, if you are a residential customer of the PGE utility in Oregon, you would receive $0.25/W up to $1,750. So for a 7 kW system you would recieve a $1,750 (7,000 W x $0.25/W) rebate.
Performance-based incentives (PBIs), also known as production incentives, provide cash payments based on the actual output of the system. For wind and solar electric, this is the number of kilowatt-hours (kWh) generated. This is usually only applied to utility-scale systems.
Rnewable portfolio standard (RPS) are very imnportant policies. Breifly, an RPS requires utilities to use renewable energy credits (RECs) to account for a certain percentage of their retail electricity sales. (RPSs are established by state legislatures, and not all states have an RPS policy.) A REC is earned by a qualified grid-tied facility for every 1,000 kWh (i.e., 1 MWh) of electricity that is generated using a renewable energy resource. The RECs are then bought and sold through a market. The settlement price varies depending on REC supply and demand at any point in time, though special auctions with guaranteed pricing and incentives are sometimes used. If you live in a state that has an RPS policy, you can "sell" your credits on an annual basis and receive a payment. For example, if you generate 7,000 kWh in a years and you can sell your credits for $40/MWh, you would earn $280 (7,000 kWh = 7 MWh x $40/MWh). You would receiv a check for this at the end of the year. See below for states that have RPS policies.
Another type of production-based incentive, a feed-in-tariff (FIT) pays grid-tied renewable energy generators a specified price for the electricity they generate and guarantees them this price for a specified amount of time. This type of policy is widely used in Europe, most notably in Germany, but less so in the USA. This is also usually used on utility-scale systems.
You may recall from EM SC 240N that bioenergy is energy that comes from living or recently living things. Common examples include wood from trees used for heating and ethanol from corn used as a gasoline additive. Another form - and one that we will see while traveling - is called anaerobic digestion. "Anaerobic" refers to "without air" and the "digestion" part refers to the microorganisms that digest organic material. Putting it together, anaerobic digestion refers to microorganisms breaking down organic material when no oxygen is present. The following descriptions of anaerobic digestion are from the EPA's Anaerobic Digestion website. All points of emphasis (bold letters) are mine:
Anaerobic digestion is the natural process in which microorganisms break down organic materials. In this instance, “organic” means coming from or made of plants or animals. Anaerobic digestion happens in closed spaces where there is no air (or oxygen). The initials “AD” may refer to the process of anaerobic digestion or the built system where anaerobic digestion takes place, also known as a digester.
The following materials are generally considered “organic.” These materials can be processed in a digester:
- Animal manures;
- Food scraps;
- Fats, oils, and greases;
- Industrial organic residuals; and
- Sewage sludge (biosolids).
All anaerobic digestion systems adhere to the same basic principles whether the feedstock is food waste, animal manures or wastewater sludge. The systems may have some differences in design but the process is basically the same
Biogas is generated during anaerobic digestion when microorganisms break down (eat) organic materials in the absence of air (or oxygen). Biogas is mostly methane (CH4) and carbon dioxide (CO2), with very small amounts of water vapor and other gases. The carbon dioxide and other gases can be removed, leaving only the methane. Methane is the primary component of natural gas.
The material that is left after anaerobic digestion happens is called “digestate.” Digestate is a wet mixture that is usually separated into a solid and a liquid. Digestate is rich in nutrients and can be used as fertilizer for crops
Biogas is produced throughout the anaerobic digestion process. Biogas is a renewable energy source that can be used in a variety of ways. Communities and businesses across the country use biogas to:
- Power engines, produce mechanical power, heat and/or electricity (including combined heat and power systems);
- Fuel boilers and furnaces, heating digesters and other spaces;
- Run alternative-fuel vehicles; and
- Supply homes and business through the natural gas pipeline
How biogas is used and how efficiently it’s used depends on its quality. Biogas is often cleaned to remove carbon dioxide, water vapor and other trace contaminants. Removing these compounds from biogas increases the energy value of the biogas...Biogas treated to meet pipeline quality standards can be distributed through the natural gas pipeline and used in homes and businesses. Biogas can also be cleaned and upgraded to produce compressed natural gas (CNG) or liquefied natural gas (LNG). CNG and LNG can be used to fuel cars and trucks.
Digestate is the material that is left over following the anaerobic digestion process. Digestate can be made into products like:
- Bedding for livestock;
- Flower pots;
- Soil amendments; and
- Fertilizers.
When properly processed, dewatered digestate can be used as livestock bedding or to produce products like flower pots.
Digestate can be directly land applied and incorporated into soils to improve soil characteristics and facilitate plant growth. Digestate can also be further processed into products that are bagged and sold in stores. Some emerging technologies can be employed post-digestion to recover the nitrogen and phosphorus in digestate and create concentrated nutrient products, such as struvite (magnesium-ammonium-phosphate) and ammonium sulfate fertilizers.
The video below from Michigan State University does a great job of explaining how they use anaerobic digestion to convert organic cafeteria and farm waste into useful energy and fertilizer. To view the transcript (and the video on YouTube, click this link [19].)
Thermodynamically speaking, the energy conversion process is:
It is extremely important to keep in mind that this is a natural process, and thus will occur any time organic material is subjected to low- or no-oxygen conditions. One important implication of this is that organic material that ends up buried in a landfill will convert partially to methane because there is very little oxygen underneath all of that "junk." As I'm sure you recall, methane is about 30 times more potent than CO2 in terms of its global warming impact. If you took the same organic material and let it biodegrade in the open air (i.e., with access to oxygen) it would release mostly CO2. The sad irony of this is that well-meaning people and companies can actually make the (climate change) problem worse if their biodegradable containers end up in the landfill. This methane can be captured, and in many places in the U.S. and throughout the world is. This is also why impoundment hydroelectric facilities (big dams) can cause methane emissions - organic material collects upstream of the dam, and low-oxygen conditions often occur near the bottom of the reservoirs, causing methane to be released. Systems thinking, everyone!
Digesters can be pretty much any size. I've seen one as small as a car inner tube that was used to power a gas grill and heat a small greenhouse. Some of them can be larger, as you'll see below.
The pictures below are from a cooperatively-owned anaerobic digester in Lemvig, Denmark. I'm particularly fond of this because the entire setup is owned equally by about 25 farmers, and is a non-profit operation. All of the organic waste from the farms is transported to the digester, including leftover vegetation and various types of manure. The biogas is used to generate electricity in a turbine which is either sold to the grid or used in the digester, and the "waste" heat is used to run the anaerobic digester. The remaining heat is used for district heating for the town - it heats up water, which is then run through underground pipes to be used to heat homes. This type of generator is considered cogeneration, which means it is used to generate electricity and useful heat. Recall that most power plants are about 35% efficient because so much energy is wasted as heat. Believe it or not, this cogeneration system is over 90% efficient when you include all of the "waste" heat that is captured and used! All digestate is then returned to the local farms and used as organic fertilizers. It is truly a closed-loop system!
The images below show details of a smaller installation in Kussnacht, Switzerland. This installation is run by a single farmer (Seppi), who collects organic waste from his farm, other local farms, and area restaurants. Like the one above, Seppi collects the biogas and uses it in a cogeneration system that is about 90% efficient (50% heat, 40% electricity, and 10% is wasted). He runs a 100 kW generator and uses the electricity on his farm and sells the leftover to the grid. The heat is used to run the digester, and to provide space and water heating to his farm. He uses some digestate on his farm and gives the rest back to local farmers for free.
It just so happened that at the time of our visit (I brought students there for a study abroad experience), his previous digester had burnt down due to a generator fire. The upshot of this is that we were able to see inside the digester he was building, which you will see below.
By now you should be able to:
You have reached the end of the lesson! Double-check the to-do list on the Lesson Overview page [20] to make sure you have completed all of the activities listed there before you begin the next lesson..
In this lesson, we'll go over some of the basics of wind and microhydroelectric energy, including how to do some basic output calculations.
By the end of this lesson, you should be able to:
To Read | Lesson 2 Online Content | You're here! |
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To Do |
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If you have any general course questions, please post them to our HAVE A QUESTION discussion forum located under the Discussions tab in Canvas. I will check that discussion forum regularly to respond as appropriate. While you are there, feel free to post your own responses and comments if you are able to help out a classmate. If you have a question but would like to remain anonymous to the other students, email me through Canvas.
If you have something related to the material that you'd like to share, feel free to post to the Coffee Shop forum, also under the Discussions tab in Canvas.
As you may recall, the wind is caused by differential solar heating across the surface of the earth (as well as the shape of the earth), which causes large- and small-scale high and low-pressure systems to form. Air moves from areas of higher pressure to areas of lower pressure, which is what causes wind to occur. (If you are interested, this National Geographic site [21] explains some of the finer points of this process, including a lot of pictures.)
Wind, then, is just air that is moving. Simply put, this air has kinetic energy because wind has mass and is moving. (Anything in motion with mass has kinetic energy.) Because of the First Law of Thermodynamics, the energy in the wind must come from somewhere else. This "somewhere else," is solar energy. This energy (and power) can be quantified. See later in this lesson for an explanation of how to calculate this.
Average wind speeds vary widely by geographical location. Take a few minutes to inspect the wind speed charts from the National Renewable Energy Laboratory below. Note the location of the greatest and smallest wind speeds, and think about the physical characteristics of those areas (e.g., flat, mountainous, on-shore, off-shore, etc.). Click here for a larger version of the 40 m wind speed image [22] and click here for the 80 m image. [23] Note that the average wind speed is higher at 80 m at the same location. Wind speed generally increases with height due to the decreasing influence of friction from the earth's surface and things on it. Modern turbines are generally tall enough to take advantage of 80 m wind speeds.
In addition to variability being a barrier to wind deployment, the location of wind resources is as well. In general - and certainly, in the U.S. - the best onshore wind resources are not located near major population centers. Approximately 50% [24] of the U.S. population lives within 50 miles of the coast, but as you can see in the maps below, this is generally not where the greatest onshore wind is located. This is a problem because transporting electricity over power lines results in energy loss (as heat) due to electrical resistance in wires. The longer the electricity has to travel, the more energy is lost. To minimize this loss, large (and very expensive) power lines must be built. As you can imagine, this type of infrastructure is lacking in areas of the country that do not have large populations.
However, it is clear from the second map that significant offshore wind resources are available very near the coast. Unfortunately, offshore wind is still expensive (remember from a previous lesson [25] that the LCOE is the highest of those listed). That, combined with resistance from local inhabitants had kept the offshore wind at bay until 2016 when the first offshore wind farm (albeit a very small one) in the U.S. was opened in Rhode Island [26]. There are over two dozen in the planning stages [27] as we speak. This is likely an area of growth in the near future.
Now for some terminology and other considerations:
See below for a diagram of key components of wind turbines:
There is a lot to digest here. The components I'd like you to know are as follows. All quoted text is from the U.S. Department of Energy [30]:
The basic energy conversion process is as follows:
Turbines come in a very wide variety of sizes and capacities. The images below show some of this. (We will see the second turbine in Golden, CO!)
The power in the wind is given by the following equation:
Power (W) = 1/2 x ρ x A x v3
Thus, the power available to a wind turbine is based on the density of the air (usually about 1.2 kg/m3), the swept area of the turbine blades (picture a big circle being made by the spinning blades), and the velocity of the wind. Of these, clearly, the most variable input is wind speed. However, wind speed is also the most impactful variable because it is cubed, whereas the other inputs are not.
The following are calculations for power available in the wind at three different velocities for the Northwind 100C turbine. This is the newer version of the Northwind 100A on the previous page. The calculations will show what happens when you double, then triple the velocity. Take a moment to think about how much available power will increase if you double and triple the velocity:
As you can see, when the velocity doubles, the power increased by a factor of 8 and when the velocity triples, it increases by a factor of 27. This is because the velocity is cubed: 23 = 8 and 33 = 27.
The output of a wind turbine is dependent upon the velocity of the wind that is hitting it. But as you will see, the power is not proportional to the wind velocity. Every turbine is different. In order to determine the output of a specific turbine at a given wind velocity, you need its power curve. The power curve and corresponding data for the Northwind 100C can be seen below:
wind speed (m/s) | 1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 | 11 | 12 |
---|---|---|---|---|---|---|---|---|---|---|---|---|
power output (kW) | -0.5 | -0.5 | 1.2 | 7.2 | 14.5 | 24.7 | 37.9 | 58.7 | 74.8 | 85.1 | 90.2 | 94.7 |
wind speed (m/s) | 13 | 14 | 15 | 16 | 17 | 18 | 19 | 20 | 21 | 22 | 23 | 24 | 25 |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|
power output (kW) | 95.3 | 95.1 | 94.2 | 92.9 | 91.2 | 88.9 | 87.1 | 84.1 | 81.3 | 78.6 | 75.1 | 74.3 | 71.7 |
As you can see, even though this is a 95 kW turbine, it only provides (approximately) that much power at a very limited number of wind speeds - about 12 m/s through about 15 m/s. Counterintuitively, the power output decreases if the wind speeds up past that point. For safety reasons, the turbine will stop spinning if the wind speed is higher than 25 m/s.
Assuming the turbine is operating properly, the output calculation is pretty straightforward. You just multiply the output at a given velocity by the number of hours the wind is blowing at that velocity. For example, let's assume that the wind hitting a Northwind 100C in a given day has the following velocities. (Note that in reality, the wind would likely change much more frequently than this. I just wanted to make the math relatively easy.):
velocity (m/s) | number of hours at that velocity |
---|---|
6 | 4 |
8 | 8 |
12 | 5 |
15 | 4 |
16 | 3 |
16 | 3 |
The total output at 6 m/s would be: 24.7 kW (the output at 6 m/s from the power curve table) x 4 hrs = 98.8 kWh.
Based on the power curve table above, the total output for this day would be:
velocity (m/s) | number of hours at that velocity | total output (kWh) |
---|---|---|
6 | 4 | 98.8 |
8 | 8 | 469.6 |
12 | 5 | 473.5 |
15 | 4 | 376.8 |
16 | 3 | 278.7 |
16 | 3 | 278.7 |
Total | 24 | 1,697.4 |
One last consideration to make for wind turbines (or any energy source) is something called capacity factor. Capacity factor indicates how much energy is generated by a source relative to the maximum amount of energy it could provide. This is expressed as a percentage, and is usually determined over the course of a single year. This provides insight into how well-sited the turbine is, but in general indicates how available an energy source is throughout the year. The closer to 100%, the more the energy source is available throughout the year.
The formula is capacity factor = actual output/maximum possible output.
For a wind turbine, the maximum possible output would be the capacity x 8760 hr (there are 8760 hrs in a year). So for the Northwind 100C, the maximum output is: 95 kW x 8760 hr/yr = 832,200 kWh/yr (or 832.2 MWh). If the actual output over the course of a year was 250,000 kWh, the capacity factor would be:
The average capacity factor of the U.S. wind fleet hovers around 32% - 34% [36], but new turbine designs have been tested in the 60%+ range, like the 12 MW behemoth [37] by GE. It's not unusual to see 40% and up capacity factors for well-sited wind farms.
Like moving air, moving water has kinetic energy (it has mass and it is moving). But water is much denser than air - this is obvious to anyone who has waded across a deep stream or played in ocean waves. If you recall, air has an average density of 1.225 kg/m3. One cubic meter of water, on the other hand, has a mass of 1,000 kg, or one metric ton (aka one tonne). It may be hard to believe, but a cube of water that is about 3.3 feet on each side weighs over 2,000 pounds!
Where does this kinetic energy come from? Take a second to think about it...Water only flows downhill, so if you see moving water it came from a higher elevation. This kinetic energy is thus converted from gravitational potential energy. How did it get this gravitational potential energy? Well, something had to take the water up to the higher elevation. The only natural way this happens is through evaporation, which is almost always caused by the sun, in a number of different ways: Water that is heated by the sun may evaporate. Wind also evaporates water, but remember that wind gets its energy from the sun. Plants evapotranspirate water, but again, they get their energy from the sun. Even the minor amount exhaled by humans is solar energy since all of our energy comes from the sun. The only major exception is that some evaporative heat is provided by geothermal energy from the earth, e.g., in volcanoes. At any rate, almost all hydropower/energy comes from the sun
Humans have been using hydropower for thousands of years [38]. According to the U.S. Department of Energy, the Greeks used water to spin wheels to grind grain over 2,000 years ago. Modern humans figured out how to convert hydropower to electricity by using a turbine and generator (see below), which is called hydroelectricity, for obvious reasons. The first known use of hydroelectricity [39] was in 1878 to power a single lamp in Northumberland, England. Larger plants were installed in 1881 in the U.S., and the first commercial-scale plant was built in the U.S. in 1893 in Redlands, California.
All hydroelectric power plants operate on the same principle. Moving water spins a turbine, which spins an electric generator. See below for an illustration of an impoundment facility, which uses a dam to create a reservoir of water.
Explaining all components in this image goes beyond the scope of this lesson. The important terms for this lesson are:
This basic process - flowing water spins a turbine, which spins a generator - is common to all types of hydroelectricity installations. There can be any number of other components, and the size/scale may be different, but this core process is the same.
Like all other electricity sources, hydroelectric power plants have a rated capacity. Large impoundment facilities can have capacities on the order of GWs (billions of watts). The largest facility in the world - the Three Gorges Dam in China - has a capacity of 18 GW. According to the U.S. Department of Energy, a microhydro system has a capacity of up to 100 kW [41]. Most systems are much smaller. A residential-scale microhydro system is more likely to be a few kWs in size.
A typical microhydro system is illustrated in the image above. Systems can vary significantly in style and size, but according to the U.S. DOE, the following components are commonly seen in most systems [44]:
As described above, the kinetic energy in flowing water starts out as gravitational potential energy. The gravitational potential energy of a given amount of water at any elevation can be calculated using the following equation:
The force of gravity is essentially a constant (it gets a little bit smaller with height). Thus, all else being equal, as height and mass increase, the potential energy increases. Keep in mind that this equation only illustrates the maximum kinetic energy available to a hydropower system. In reality, there are always losses by the time the kinetic energy is converted to electricity.
The power available in water at height is given by a similar equation:
Again, this is only the hypothetical maximum - it is impossible to capture all of this power in a turbine. This equation is almost the same as the potential energy equation - you just substitute discharge for mass. Since the discharge is kg/s, or mass divided by time, if you compare the two equations, the power equation is the energy equation divided by seconds. This makes sense if you think about it: the potential energy is given in Joules, and the power equation is given in watts. Recall that 1 J/s = 1 W. Makes sense, right?
It turns out that calculating the approximate power output of a microhydro system is not terribly difficult. According to the U.S. DOE, a typical system has an efficiency of about 53%. This includes losses from the nozzle, the wiring, the generator, and a few other things. The power of a microhydro system with this efficiency is approximately:
To determine the gross head, you measure how many feet above the generator the penstock starts. Note that this is not the same as the length of the penstock. The penstock is sloped, and thus will be longer than the head. The head loss is based on a few factors, including the diameter of the penstock, the pressure inside the penstock, and the number of turns and fittings there are in the penstock. According to Homepower Magazine, 30% is a typical amount of head loss, which means you would calculate the gross head time 0.7 to determine the net head. The flow of a stream through a penstock can vary wildly, from a few gallons per minute to a few hundred (or more). To provide some context a garden hose usually has a flow of about 20 gallons per minute, though this can also vary significantly depending on a number of factors.
Let's say I have a property in which I can create a diversion channel and forebay 100 ft above a power house, and I measure my flow at 50 gpm. Assuming a good system design which includes a head loss of 30%, my output would be:
This lesson only scratches the surface of microhydro systems. There are many designs and factors to consider. Each site is different. For a more detailed explanation, see this website from the U.S. DOE [45], and for a good case study, see this example from Homepower Magazine ( [46]starting on p. 32). There are dozens of videos on YouTube that detail specific systems, many of which are worth checking out if you are interested.
If you are interested in learning more about the power and energy available in water for hydroelectric, see this video presentation I put together [47]for another course.
Starting this week and moving forward — each week, I will provide links to some of the locations/organizations we will visit. This is not required reading. I suggest browsing through them if/when you have time. This may help inspire your final project proposals!
By now, you should be able to do the following:
You have reached the end of Lesson 7! Double-check the to-do list on the Lesson 7 Overview page [52] to make sure you have completed all of the activities listed there before you begin Lesson 8.
The focus of this lesson is on ways to sustainably manage natural resources.
By the end of this lesson, you should be able to:
To Read | Lesson 8 Online Content | You're here! |
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If you have any general course questions, please post them to our HAVE A QUESTION discussion forum located under the Discussions tab in Canvas. I will check that discussion forum regularly to respond as appropriate. While you are there, feel free to post your own responses and comments if you are able to help out a classmate. If you have a question but would like to remain anonymous to the other students, email me through Canvas.
If you have something related to the material that you'd like to share, feel free to post to the Coffee Shop forum, also under the Discussions tab in Canvas.
I'm sure you've heard the term "natural resources" used many times, e.g., when someone talks about "preserving natural resources" or when you hear about "natural resource management." It's a pretty innocuous term, and seemingly straightforward. If you asked someone what natural resources are, they would probably say something about "resources provided by nature, such as trees, minerals, and food" or something to that effect. (This is actually a pretty good definition, by the way!) When thinking about the definition, it's easy to focus on the "nature" component and look past the "resources" part. Specifically, it is important to note that "natural resources" is an anthropocentric (human-centered or focused) term. It is a concept that only exists because of humans because it refers to things that impact humans. To demonstrate this, let's look at a few definitions of natural resources:
things such as minerals, forests, coal, etc. that exist in a place and can be used by people
~Cambridge Dictionary [53]
industrial materials and capacities (such as mineral deposits and waterpoer) supplied by nature
~Merriam-Webster [54]
a naturally occurring source of wealth, as land or water; the natural wealth of a country, consisting of land, forests, mineral deposits, water, etc.
~dictionary.com [55]
Any way you slice it, without humans natural resources don't exist, they would just "be" or just be "nature." This is important to keep in mind as we go over this lesson: by definition, natural resources only exist as a concept because they can be used by humans.
Personal consumption expenditures (household spending on goods and services) constitutes nearly 70% of U.S. GDP [56]. Much of this is on services, but Americans now spend over 5.5 trillion dollars on "goods," which includes everything from food, to energy, to cars, houses, clothing, and other goods. See the charts below from the Federal Reserve Bank of St. Louis [57] for these consumption trends over the past 60+ years. They are an excellent, reliable resource for economic data. (For a good explanation of goods and services, see this explanation [58]from thebalance.com.)
The moral of the story: Americans buy a lot of stuff! This has many implications, but one is particularly important with respect to this lesson. Namely, almost all of this spending requires the use of natural resources. Obviously, things like cars and clothes require raw natural resources to produce, though you may be surprised at how many. Take a look at the infographic below from Allianz to get some idea of how many different natural resources from all over the world are needed to make a car.
Infographic by:All goods require some mixture of raw natural resource extraction, manufacturing, processing, shipping, packaging, use, and disposal. All of this requires energy and resources. Most of this use, as indicated in the infographic above, is hidden.
I will give you one more quick example: I used to assist with industrial energy audits on a part-time basis while in college. One of the places we audited was a "feed mill," which is essentially a factory that produces chicken feed. (Related note: Delaware is considered the poultry capital of the U.S.) The facility looked a lot like the one in the image below.
I was dumbfounded at how much energy and resources went into just producing feed for chickens! While I was there, there was a constant arrival of tractor trailers hauling raw ingredients - corn, soybean, nutrient mixes, and other things - and the machinery was massive and energy-intensive. According to Delmarva Poultry Industry, Inc. [65] (Delmarva includes parts of Delaware and the eastern shores of Virginia and Maryland), the Delmarva chicken industry had the following specifics in 2020:
The point here is not to go in-depth into the poultry or automobile industries, but to indicate that nearly everything you purchase is the product of a tremendous use of resources, much of which is hidden. But services such as healthcare and education also require the use of resources. Medical facilities need chairs, tables, x-ray machines, paper, and so forth, use a lot of energy, and create an immense amount of waste. Even an online class requires physical resources, in particular, electricity (e.g. cloud-based storage uses [66]about 70,000 - 140,000 times the energy of storing data on your computer), and all of the lifecycle resources used to generate that energy (mines, power plants, power lines, equipment to manage it all, etc.), but also the device you are viewing this on is the result of a global supply chain of goods, and there are natural resource impacts at every step of this supply chain. This type of lifecycle resource use and our consumption-driven economy are major contributors to the fact that we would need nearly 5 planet earths to satisfy humanity's needs if everyone lived like the average American.
The problems associated with the massive amount of resources used to produce everyday goods and services is compounded by the fact that this system is based mostly on linear resource use. This is often referred to as "take, make, waste." An illustration of the basic resource flow is shown below.
This linear model typically goes something like the following:
This model requires the constant input of raw natural resources because of the waste and emissions along the way, and because most of the "waste" is dumped in a landfill (and possibly incinerated), and all of this is done primarily with the use of non-renewable energy. This is a major reason why our ecological footprint is so large and we are using natural resources at such a high rate. Globally, only about 12.5% [68] of the primary energy used is renewable (source: BP 2021 Statistical Review of World Energ [69]y). In the U.S., over half of municipal solid waste (MSW) ends up in a landfill. Keep in mind that municipal solid waste is basically household garbage, and does not include construction, industrial, or farming waste, which make up a large portion of the waste stream. All of this adds up to 292.2 million short tons of MSW generated (about 4.9 pounds per person per day, which is up from 4.5 pound per person per day a few years ago), of which about 146 million tons ends up in a landfill, according to the U.S. EPA [70].
Contrast this with a circular resource flow model, in which there is almost no waste. Any resources that are unused in each step are reintegrated back into the system. Manufacturing "waste" is reused or recycled, as are final products used by the end user. If this could all be run using renewable resources, then much of the pollution would be eliminated as well. In fact, in an ideal circular resource system, the idea of "waste" does not exist. This is the philosophy behind "zero waste" initiatives. Note that because of thermodynamics, there will be some inefficiency, and thus some loss. This is why there will still be some natural resource input required.
It is worth noting that nature utilizes circular resource flow. Recall that it was stated above that the concept of natural resources is anthropocentric. There is no waste in nature - everything is a resource for some other process. Resources move around in continuous flows, and all "waste" is reintegrated back into the system, with the exception of some heat loss that is radiated back to space. All of this is of course driven by renewable energy, and any energy lost to space is offset by energy coming in from the sun. This is why many zero waste (and other sustainability) advocates say that the more we can design human systems to mimic natural systems, the more sustainable those systems will be. As you will see in a future lesson, this is the fundamental philosophy of permaculture.
The Zero Waste Alliance provides an excellent visualization of what such a system could look like. The images below show natural resource flows. The thickness of the flows indicates the relative amount of resources flowing through that part of the system. As you can see, by recovering most of the "waste" throughout, the raw materials flow (at the far left of each diagram) is greatly reduced. Note that the second image shows an idealized flow - there will be some loss due to thermodynamics. Even without thermodynamic loss, some natural resource extraction is required because some resources cannot be directly reused in the manufacturing process.
No doubt you have seen some variation of the image below. Most recyclable packaging has a triangle design, which indicates that it is recyclable. You are probably familiar with the phrase "reduce, reuse, recycle," which is hammered home to (most) kids at a very early age in the U.S. The image clearly gives a nod to circular resource use (follow the arrows!). Each term refers to a slightly different way to manage waste. I provide an example of each in parentheses as it relates to a plastic water bottle:
However, what most people do not know is that "reduce, reuse, recycle" is actually a priority list. In other words, the best way to minimize the impact of waste is to not use it in the first place (reduce), the second best way is to reuse it, and the third best way is to recycle it. Recycling requires a lot of inputs: inefficient trucks to pick it up and transport it, massive machinery to sort it and break it down, more machinery to produce the new good (often after shipping the raw resource far away), then more energy and resources to distribute the good. This entire process uses energy and generates waste. Reuse is less impactful because it cuts out all of the downstream impacts of recycling, but it does not eliminate all of the upstream impacts that resulted from producing the good in the first place.
While all of this is true, recycling is still much more beneficial than landfilling! The following are some statistics from the EPA [73]. All information was taken from WARM, the Waste Reduction Model. (Click here to download the Excel file [74] and do your own analysis, or just explore the data.) Note that MMBTU is one million BTUs of energy, and MTCO2e refers to one megaton of carbon dioxide equivalent:
material | reduction energy savings (MMBTU/ton) | recycling energy savings (MMBTU/ton) | combustion energy savings (MMBTU/ton) | reduction emissions savings (MTCO2e/ton) | recycling emissions savings (MTCO2e/ton) | combustion emissions savings (MTCO2e/ton) |
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aluminum cans | 89.69 | 152.76 | -0.60 | 4.91 | 9.11 | -0.04 |
glass | 6.9 | 2.13 | -0.50 | 0.53 | 0.28 | -0.03 |
PET plastic | 50.26 | 31.87 | 10.13 | 2.20 | 1.12 | -1.21 |
corrugated cardboard | 33.23 | 0.69 | 6.64 | 5.60 | 3.12 | 0.51 |
newspaper | 36.46 | 16.49 | 7.53 | 4.77 | 2.75 | 0.58 |
Notice that with the exception of aluminum cans, the energy and emissions reductions are always greater when you reduce than when you recycle. Based on what I could see in the WARM spreadsheet, aluminum cans are the only material for which recycling is more impactful. Also note that some materials require more energy to burn than they do to landfill (see the negative numbers), and for ALL materials listed, combustion is worse for emissions than recycling or reducing.
The circular economy, as you will see below, utilizes circular resource use.
There are a few ideas underlying the circular economy concept, as described in the videos:
The MacArthur Foundation notes that the circular economy is "about a rethinking of the operating system itself." This is a very important point! The take-make-dispose process is systemic, and is deeply ingrained in society. If we are to get past this mindset, systemic change is required.
Of course, we are socialized to believe that ownership is important (Americans in particular love buying stuff), so the establishment of a circular economy will require social change. This may seem a difficult hill to climb. Well, it is, actually, but allow me to provide one example of why it may be more feasible than you think. Consider the ubiquity of Uber and Lyft. It may be difficult to imagine, but try to think back 10 years ago, before ridesharing existed. Treating automobile transportation as a service was mainly reserved for taking cab rides in cities. Now you can take an Uber in 85 countries [76] across the world, and the service is available even in rural areas of the U.S. The point here is not that Uber and Lyft are examples of the circular economy (though they do minimize the necessity of automobile production), but that personal transportation is increasingly being viewed as a service. It is a rather commonly held belief [77] that autonomous vehicles will reduce vehicle ownership. Rideshare and car companies are already testing driverless vehicles, and in the not-too-distant future, they will increasingly own their own vehicle fleet instead of paying others to drive, or in the case of car companies, expecting consumers to buy their cars. If/when that happens, it will be to their benefit to extend the use of their fleet as long as possible.
Please watch the video below for some insight into an application of the circular economy called Cradle to Cradle Design. (5:49 minutes)
As you can see, cradle to cradle (C2C) concept is an application of the circular economy. The concept is summed up rather well in the video when they state that C2C is all about "keeping all materials in continuous cycles, stimulating the use of renewable energy only, and celebrating diversity," though there is more to it, as you will see below. The following are some of the key points from the video above:
The Cradle to Cradle Products Innovation Institute [79] has taken this concept beyond the conceptual phase and created a process to certify products using their Cradle to Cradle CertifiedTM product standard [80]. The standard is described as follows:
The Cradle to Cradle Certified [81]™ Product Standard [81] guides designers and manufacturers through a continual improvement process that looks at a product through five quality categories — material health, material reutilization, renewable energy and carbon management, water stewardship, and social fairness. A product receives an achievement level in each category — Basic, Bronze, Silver, Gold, or Platinum — with the lowest achievement level representing the product’s overall mark.
Product assessments are performed by a qualified independent organization trained by the Institute [82]. Assessment Summary Reports are reviewed by the Institute, which certifies products meeting the Standard requirements, and licenses the use of the Cradle to Cradle Certified™ word and design marks to the product manufacturer. Every two years, manufacturers must demonstrate good faith efforts to improve their products in order to have their products recertified.
The five quality categories [83] are as follows:
Material Health: Knowing the chemical ingredients of every material in a product, and optimizing towards safer materials.
Material Reutilization: Designing products made with materials that come from and can safely return to nature or industry.
Renewable Energy & Carbon Management: Envisioning a future in which all manufacturing is powered by 100% clean renewable energy.
Water Stewardship: Manage clean water as a precious resource and an essential human right.
Social Fairness: Design operations to honor all people and natural systems affected by the creation, use, disposal or reuse of a product.
If a product would like to go for C2C certification, it is evaluated based on these five categories. It receives a score in each category - basic, bronze, silver, gold, or platinum. These are also the five levels of cradle to cradle certification. The certification level is based on the lowest score that the product receives in these categories. For example, if a product earns a "gold" score in material health, material reutilization, renewable energy & carbon management, and water stewardship, but only earns a "basic" score in social fairness, then the product is certified as "basic." Another important aspect to point out is that all products must be recertified every two years, and in that time, must demonstrate good faith efforts to improve the products.
By now, you should be able to do all of the following:
You have reached the end of Lesson 8! Double-check the to-do list on the Lesson 8 Overview page [84] to make sure you have completed all of the activities listed there before you begin Lesson 9.
The focus of this lesson is to consider the negative sustainability impacts of food production, and investigate solutions to these problems.
By the end of this lesson, you should be able to:
To Read | Lesson 9 Online Content | You're here! |
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If you have any general course questions, please post them to our HAVE A QUESTION discussion forum located under the Discussions tab in Canvas. I will check that discussion forum regularly to respond as appropriate. While you are there, feel free to post your own responses and comments if you are able to help out a classmate. If you have a question but would like to remain anonymous to the other students, email me through Canvas.
If you have something related to the material that you'd like to share, feel free to post to the Coffee Shop forum, also under the Discussions tab in Canvas.
Other than energy, it is through food that most of us most frequently directly interact with sustainability. Humans cannot survive without food, and most (and probably all) of you reading this eat multiple meals each day. The food industry has immense sustainability implications, including soil health and conservation, water use, forest clear-cutting, environmental and social justice, economics and equity, and much more. The following provides some insight into a few of these issues.
You probably recall from a previous lesson that irrigation is the single biggest user of freshwater in the United States. You may also recall the large water footprint of some common foods. The following are footprints of common main dishes, according to the Water Footprint Network [85] (see Water Footprint report [86]). (Note that these are global averages. Also, 1 litre/kg equals about 0.12 gal/lb.):
If you are interested, the Huffington Post does a nice job of comparing the water footprint of common foods [87]. (They use Water Footprint Network data.)
Almost all of the water used in producing meat is the result of irrigating the crops that are used to feed the animals, and some irrigation methods are more efficient than others. (Oregon State University Cooperative Extension provides a good analysis of various irrigation techniques [88] if you are interested in learning more.)
One sustainability impact that happens on more of a macro scale is something called a "dead zone." The National Oceanic and Atmospheric Administration (NOAA) explains dead zones [89] thus:
Less oxygen dissolved in the water is often referred to as a “dead zone” because most marine life either dies, or, if they are mobile such as fish, leave the area. Habitats that would normally be teeming with life become, essentially, biological deserts.
Hypoxic zones can occur naturally, but scientists are concerned about the areas created or enhanced by human activity. There are many physical, chemical, and biological factors that combine to create dead zones, but nutrient pollution is the primary cause of those zones created by humans. Excess nutrients that run off land or are piped as wastewater into rivers and coasts can stimulate an overgrowth of algae, which then sinks and decomposes in the water. The decomposition process consumes oxygen and depletes the supply available to healthy marine life.
Dead zones occur in many areas of the country, particularly along the East Coast, the Gulf of Mexico, and the Great Lakes, but there is no part of the country or the world that is immune. The second largest dead zone in the world is located in the U.S., in the northern Gulf of Mexico.
Dead zones happen all over the world and are in fact a natural occurrence. However, humans have significantly increased the incidence of dead zones, including the one in the Gulf of Mexico, which grows to about the size of New Jersey every summer, as you will see in the video below. These dead zones are caused by eutrophication, which is when a body of water has an excessive amount of nutrients (primarily nitrogen and phosphorous) that lead to unusually high plant/algae growth. (Note that eutrophication just refers to excess nutrients, but this often results in a dead zone.) When eutrophic streams and rivers empty into ponds, lakes, or other open bodies of water (such as the Gulf of Mexico), it causes excessive algae growth and ultimately leads to anoxic ("oxygen-less") conditions near the bottom of these bodies of water. NOAA does a good job of explaining eutrophication in the video below.
Eutrophication has a few anthropogenic causes, but the primary one is the use of artificial fertilizers on farms. Fertilizers feed plants, but if they get into bodies of water they feed algae. The video below from NOAA provides a good explanation of this. Please note that the explanation at the end of the video of what causes the dead zone is incomplete: waste from organisms that eat the phytoplankton plays a role in the dead zone, but (as described in the video above) the main cause of dead zones is when bacteria eat the dead phytoplankton after they sink to the bottom.
Over the past 10 - 15 years, food deserts have (slowly) become a more prominent issue. The following is a summary from the U.S. Centers for Disease Control [90] (emphasis added):
Food Desert
Food deserts are areas that lack access to affordable fruits, vegetables, whole grains, low-fat milk, and other foods that make up a full and healthy diet (1). Many Americans living in rural, minority, or low-income areas are subjected to food deserts and may be unable to access affordable, healthy foods, leaving their diets lacking essential nutrients.What's the Problem?
Rural, minority, and low income areas are often the sites of food deserts because they lack large, retail food markets and have a higher number of convenience stores, where healthy foods are less available (2). Studies have shown that food deserts can negatively affect health outcomes but more research must be done to show how that influence occurs. There appears to be a link between access to affordable nutritious foods and the eating of these foods, meaning less access may lead to less incorporation of healthy foods into the populations’ diets.Who's at Risk?
Because there is no standard definition of a food desert, estimates of how much of the population is affected vary by quite a bit. However, it’s safe to say that many Americans have limited access to affordable nutritious foods because they do not live near a supermarket or large grocery store. Transportation is specifically part of the USDA food desert definition. Only common theme among food desert definitions is that there is limited access.Can It Be Prevented?
Food deserts can be improved through several different types of efforts. Establishing a community garden where participants share in the maintenance and products of the garden and organizing local farmers markets are two efforts that community members themselves can do (3, 4). Local governments can improve local transportation like buses and metros to allow for easier access to established markets (5). They can also change zoning codes and offer economic or tax incentives to attract retailers with healthier food offerings to the area (6).The Bottom Line
Food deserts are a big problem for many Americans that may limit their ability to eat healthy and nutritious foods on a regular basis. However, there are a variety of ways that local governments and community members can both improve food access in their neighborhoods.Case Example
Maria is a 60-year-old woman living in a low-income area of St. Louis. As she’s gotten older, she hasn’t been able to get around as well and doesn’t have a car. She usually eats a lot of unhealthy and microwavable foods because the closest store to her apartment is the local convenience store around the corner. She wishes that she could eat better and begins talking to some of her neighbors and other families in the building to get their input. Maria and her next-door neighbor Sylvia organize all the residents in their building to establish a community garden on the roof of the building so that they will all have fresh fruits and vegetables to share.
As indicated above, there is no one definition of a food desert, but it is meant to indicate a lack of access to fresh foods. The U.S. Department of Agriculture (USDA) considers three ways to define a food desert [91]. (The number of people in the U.S. in each category as of 2017 are in parentheses.):
The USDA has created a Food Access Research Atlas (available here) [92], where you can explore food deserts across the U.S. Feel free to tool around with it. (You will have to explore it for this week's quiz.)
A topic closely related to food deserts is food insecurity. The USDA defines food insecurity [93] and very low food security as follows:
The USDA provides an annual report and analysis on food insecurity in the U.S. through its Economic Research Service. Highlights (okay, lowlights) from the "Household Food Security in the United States 2017 [94]" report summary (full Household Food Security [95]report available here [95]) include:
Permaculture is another one of those concepts that have no single definition, but I like the succinct definition offered by Geoff Lawton [96], one of the more well-known permaculture teachers and practitioners in the world when he stated that permaculture is "a system of design that provides all of the needs for humanity in a way that benefits the environment." Another way to describe it is "designing human systems to mimic natural systems" and "designing systems that work with nature instead of against it." No matter how you define it, it refers to a design system - it integrates concepts from a wide array of disciplines/topics (hydrology, soil science, biology, ecology, renewable energy, forestry, and more) - and utilizes them when designing systems, such as gardens, farms, houses, neighborhoods, and more. It is most commonly used to design food systems, though. Everything from a backyard garden to a large farm can be designed using these principles.
The concept and term "permaculture" was coined by Bill Mollison and David Holmgren in Australia in the 1970s. It was originally a concatenation of the terms "permanent agriculture" because it initially focused on food production systems, but came to be known as a shortened form of "permanent culture" because it can be used to address all aspects of human culture/settlements.
The Permaculture Research Institute provides an excellent one-page description of permaculture. Please read through it before continuing.
The following are some highlights from the reading:
I want you to consider one additional concept that is mentioned in this summary. They mention that permaculture helps establish resilience. Resilience can be thought of as the ability to return to an original state after encountering a shock to the system. This has become a major focus of sustainability efforts. People recognize that "bad" things such as climate change, oil price spikes, and economic collapse will happen, but we do not know when. Much effort in sustainability design, thought, and policy is focused on establishing resilient communities (and cities, states, and countries) that will be able to withstand such shocks in such a way that suffering and distress will be minimized.
From a climate change perspective, this is primarily a focus on adaptation, i.e., adapting our communities to thrive in an uncertain climate future. This usually involves things such as using renewable energy (and not relying entirely on the national grid, e.g.), producing food locally (instead of relying on world markets), mitigating and/or avoiding flooding in low-lying areas, using more low-carbon transportation methods (e.g., bike and pedestrian infrastructure) and in general becoming more self-sufficient. This is a major focus of the Transition Town movement [98], but cities, towns, and states/provinces all over the world have engaged in planning for resiliency. For example, the state of Colorado has its own Resiliency Resource Center [99], which is operated out of the Department of Local Affairs.
The video below summarizes a lot of these concepts and adds a few others. It also provides a few examples of permaculture.
Most of this reiterates much of what is written above, but there are a few more things I'd like to point out:
Hopefully, by now you have a solid understanding of what permaculture is, as well as its core ethics. Permaculture also has a set of 12 principles that should be used to guide all design decisions. The video below from Oregon State University provides a good overview of these principles, and examples of how they can be applied. You will not be expected to memorize them, but it will be helpful to have a general understanding of each.
Permacultureprinciples.com provides an excellent in-depth explanation [100] of each of these principles and also provides a ton of examples of each principle. If you want to explore any of the principles more (this is optional but strongly suggested if/when you have some time), including examples of concrete applications, click on the links to each item below. They even have a song for each principle, which is a nice touch! All quotes are taken from the permacultureprinciples.com site.
One other thing that I'd like to note before moving on is that while remembering and applying these principles takes a lot of effort, a properly designed permaculture system significantly minimizes effort once it is established! For example, a well-designed permaculture garden will require almost no active watering (it should be rain-fed), does not require the constant addition of fertilizers (it should be mostly self-sufficient), does not need pesticides (most pests should be eliminated by beneficial insects, chickens, or other natural biological solutions, and things like proper air flow and sunlight), and it minimizes replanting (true permaculture uses mostly perennials, not annual plants). A properly designed urban environment will optimize the use of local resources such as renewable energy, local food sources, and low-impact transportation. Such an urban system should also provide resources to help all people thrive, thus minimizing the need for social services.
Please note that people spend their whole lives researching and applying permaculture - we are only scratching the surface! But hopefully, you have a reasonably good understanding of what permaculture is and how it can be applied. The following is a brief summary of some key points:
Permaculture provides a practical framework for addressing food sustainability issues, but there are many other specific practices and concepts that can contribute solutions as well. See below for a description of a few of them. There are many more than this, but these are some that we may/will encounter when traveling.
Regenerative agriculture is closely related to permaculture, but not all permaculture food production systems are regenerative. As you might guess, regenerative agriculture refers to food growing methods that improve the natural environment, i.e., they regenerate local ecosystems. Terra Genesis International [113] provides a great synopsis of this concept. Note their use of the term ecosystem services. (If you are so inclined, they have more information on their site.):
Regenerative Agriculture is a system of farming principles and practices that increases biodiversity, enriches soils, improves watersheds, and enhances ecosystem services.
Regenerative Agriculture aims to capture carbon in soil and aboveground biomass, reversing current global trends of atmospheric accumulation.
At the same time, it offers increased yields, resilience to climate instability, and higher health and vitality for farming and ranching communities.
The system draws from decades of scientific and applied research by the global communities of organic farming, agroecology, Holistic Management, and agroforestry.
Common techniques include planting native crops that enhance biodiversity, using biochar to improve soil quality and sequester carbon, integrating animals and crops into a self-sufficient system, only using organic farming methods, and more. Like permaculture, regenerative agriculture recognizes that these systems will provide feedback and change over time and that farmers must be ready to adapt their systems as needed.
Community gardens are defined by the USDA [114] as "plots of land, usually in urban areas, that are rented by individuals or groups for private gardens or are for the benefit of the people caring for the garden." Community gardens can take on many forms, but the most common one consists of any number of individual beds (from a few to a hundred or more) that are tended by individuals or groups. Most community gardens are structured such that each bed is "rented" out for a nominal annual fee, and the renter manages their bed. Community gardens typically supply water and soil, and sometimes resources such as seeds and labor assistance. They are usually overseen by a manager, but they often host group events and expect individual gardeners to help out with tasks that benefit the whole garden community. These are most common in urban areas where residents do not possess adequate space to grow their own food but can be found in many other areas. They can be found all over the world. Most gardens have a set of rules governing them, such as the types of plants they can grow and what they can use in their beds (e.g., by only using organic growing methods).
Community gardens can also take the form of school gardens located on or near school property. They can be established in elementary, middle, high school, and college environments. The goals of school gardens usually include garden, food, and/or nutrition education, though many urban gardens provide this service as well. Therapy gardens are sometimes established so that they can be accessed by people with physical and/or mental issues, as gardening has therapeutic effects. Many gardens include initiatives to grow food to donate to local organizations such as food banks.
Research has shown that there are many benefits to community gardens, including but not limited to the following. (All links originally gathered from North Carolina State University Cooperative Extension [115]:
There are many more studies that demonstrate the benefits of community gardens. If you have ever participated in one, you would probably be able to list a few more! It is important to note that research shows that the benefits of community gardens are particularly pronounced in low-income areas, and thus are a recognized strategy to address equity and social justice (but also environment and economy!).
You may have encountered Fair Trade goods such as coffee or chocolate when food shopping, or perhaps at a coffee shop. A fair trade good usually has a distinctive logo such as the one below. The purpose of fair trade certification is primarily to ensure that the workers throughout the supply chain were paid a fair wage. These certifications are affirmed by third-party certifiers that have no affiliation with the product at hand. They investigate the entire supply chain of the product and certify the product if it meets their standard.
One of the most common certifiers is Fair Trade Certified [122]TM (I cannot show their logo due to copyright.) They list [123] the following four standards that must be met in order to obtain certification:
- Income sustainability: ...Our standards ensure producers, workers, farmers, and fishermen have the money needed to invest in their lives and their work.
- Empowerment: Fair Trade empowers people to make choices for the good of themselves and their community, regardless of gender, status, position in society, or position on the globe. Rigorous standards give farmers, workers, and fishermen a voice in the workplace and the community.
- Individual and community well-being: ...Our model is fueled by committees of farmers, workers, and fishermen who decide how to invest the Fair Trade Premium based on their community's greatest needs: often clean water, education, and healthcare.
- Environmental stewardship: ...Our standards work to keep the planet healthy for generations to come by prohibiting the most harmful chemicals and taking measures to protect natural resources.
As you can see, fair trade can address issues beyond providing living wages. Generally speaking, it is better to buy fair trade certified goods than non-certified goods, but it is best to investigate individual certifiers to ascertain how legitimate they are.
Merriam-Webster [124] provides a good definition of appropriate technology:
technology that is suitable to the social and economic conditions of the geographic area in which it is to be applied, is environmentally sound, and promotes self-sufficiency on the part of those using it.
The use of appropriate technology is a particularly important consideration when providing assistance to low income or otherwise marginalized communities. The idea behind appropriate technology is to make sure that any solutions proposed and/or aid provided is appropriate for the local conditions. These "conditions" can include local natural resources, but very often include local human capital, such as local knowledge, expertise, and physical capabilities. As indicated in the definition, it must promote self-sufficiency (which goes hand-in-hand with the first point).
For example, if a well-meaning organization travels to rural Mongolia or Peru to install a solar array and provide electricity, they must consider whether the locals that they are trying to help have the expertise to repair the system if it breaks down. Perhaps there is existing local expertise, or perhaps they need to be trained. Also, can they get replacement parts if they are needed? Are the solar arrays and components at risk for damage due to local wildlife or human populations? These are all questions that must be asked if self-sufficiency is to be addressed. One of the best ways to utilize appropriate technology is to work with the local populations to help them come up with solutions, instead of telling them what to do. Most likely they will have a wealth of knowledge to offer regarding the local conditions (they live there, after all!), but they likely also have experience trying to implement solutions.
The National Center for Appropriate Technology [125] in the U.S. provides a number of examples and explanations if you are so inclined. They work primarily with low-income populations in the U.S. to provide services such as energy assistance and sustainable, local food systems.
Here are some more site visits! Again, this is not required reading. I suggest browsing through them if/when you have time. This may help inspire your final project proposals!
By now you should be able to do all of the following:
You have reached the end of Lesson 9! Double-check the to-do list on the Lesson 9 Overview page [130] to make sure you have completed all of the activities listed there before you begin Lesson 10.
Add stuff here...
The focus of this lesson is on ways to evaluate the sustainability of buildings.
By the end of this lesson, you should be able to:
To Read | Lesson 5 Online Content | You're here! |
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If you have any general course questions, please post them to our HAVE A QUESTION discussion forum located under the Discussions tab in Canvas. I will check that discussion forum regularly to respond as appropriate. While you are there, feel free to post your own responses and comments if you are able to help out a classmate. If you have a question but would like to remain anonymous to the other students, email me through Canvas.
If you have something related to the material that you'd like to share, feel free to post to the Coffee Shop forum, also under the Discussions tab in Canvas.
I am going to start this lesson with a very simple question: What is the purpose of a building? The U.S. EPA says that [131]Americans spend on average around 90% of their lives indoors, so there must be a good reason to use them. Please think about an answer before moving on.
When you think about it, the use of buildings boils down to two primary objectives. In no particular order, these are 1) safety/securty and 2) to control the climate and to "keep nature out" of the building. There is no disputing the need for safety, from the earliest human habitations to modern buildings. Climate control is of course very important as well: Most of the things you do in buildings - eating, sleeping, gathering with family or friends, getting work done, relaxing, etc. - often require, or at least are much easier to accomplish with, some form of climate control. Have you ever tried to get a good night's sleep in a cold, pouring rain with no shelter, get some work done on your computer in the middle of an unbearably hot, humid, sunny day, or try to read a book on a cold, windy winter day? I can't say that I have, but I know it would not turn out well.
Over time, humans have gotten better and better at controlling the climate inside of buildings. While some ancient societies clearly understood the benefits of using natural means to make buildings more comfortable and minimize heating, cooling, and lighting needs (as you will see below), in the U.S. it was not until 1978 [132]that there was any federal requirement for states to enforce energy efficiency in new buildings. Two consistent feature of colonial-era buildings in the U.S. is that they were cold (they did not hold heat well in the winter) and drafty (aka leaky). This is not unique to the U.S. The United Kingdom, for example, has some of Europe's oldest building stock [133] (that is saying something, considering how old most European cities and towns are!). About 50% of residential buildings and 39% of non-residential buildings in the UK were built before energy standards were widely introduced in the 1970s (source: RICS [134]). There have been major movements in recent decades [135] to reduce energy use in UK buildings, with limited success.
That stated, buildings built after the 1970s have generally become more efficient, largely due to increasingly robust energy standards in the U.S. [136] required by the federal government (though some states, e.g. California, consistently have more stringent standards than required). Most of these codes are based on international energy standards such as the International Energy Conservation Code [137] (IECC). Technology related to things such as insulation, air sealing, and high performance windows has also improved.
Generally speaking, we are headed in the right direction in terms of energy efficiency of buildings. But anecdotal evidence and published research indicate that there are still an abundance of opportunities to improve energy efficiency. One important consideration ist that a lot of existing houses in the U.S. and elsewhere were built before energy standards were implemented. I can tell you from personal experience and from talking to folks that have been in the industry for decades that any building - commercial or residential - that was built around or before 1980 (unless it has been retrofitted) has negligible insulation and is very leaky. Modern buildings must be more efficient because of codes but are still usually built with the idea that we should just use technology such as heating and cooling equipment, insulation, air sealing, and lighting to reduce energy usage. The overall point is that very little consideration has been given to how the building can utilize the surrounding natural conditions to reduce energy usage and increase occupant comfort. Enter passive design principles.
Before moving on to learn about passive design, please read the following articles about the benefits of energy efficiency.
It is a widely agreed-up fact that the sun provides enough energy every hour to provide all of humanity's energy needs for one year. Thus, it stands to reason that there is likely enough sunlight to provide the average household's energy needs throughout the year. We will save that calculation for a later time, but some related research from the National Renewable Energy Laboratory (NREL) has shown that much of the electricity in the U.S. could be provided by solely installing PV arrays on suitable rooftops in the U.S. The images below show 1) the percent of buildings in each state that have suitable rooftop space and 2) the percent of the total electricity sales that could be provided by suitable rooftop space in each state. You can read the full report here [146]if interested.
Passive design - including passive solar design - seeks to minimize heating, cooling, and lighting energy use in a building using passive strategies. Before we begin, please note the difference between passive and active solar design, as described by the California Energy Commission [147]:
"Homes constructed with passive solar design use the natural movement of heat and air to maintain comfortable temperatures, operating with little or no mechanical assistance. It's called passive solar because the design of the home maximizes the benefits it receives from the sun with standard construction features. Passive solar takes advantage of local breezes and landscape features such as shade trees and windbreaks, and uses a simple system to collect and store solar energy with no switches or controls.
On the other hand, active solar systems use mechanical devices such as pumps and fans to move heat from collectors to storage or from storage to use. Photovoltaic panels that collect solar energy, turning it into electricity, are also considered an active solar system."
It is important to distinguish between passive and active strategies. While active strategies such as solar PV and high-efficiency heating and cooling equipment are essential components of minimizing energy use and reliance upon unsustainable energy sources, passive design requires a different mentality and in some ways, design intent. For example, many homes in the U.S. have enough roof (and/or yard) space to accommodate enough solar PV modules to provide all of their electricity needs even if the houses were not originally designed with that intent. This is especially possible if the home upgrades to highly efficient heating and cooling, as well as improved insulation and air sealing. However, it would be difficult for most houses in the U.S. to become truly passive, because passive design principles are more specific than simply having enough properly-oriented roof or yard space.
Though you may see some minor disagreements on these depending on which source you use, the following are generally accepted to be essential passive solar design principles. It is important to note that you can minimize energy use by selectively implementing these, but in order for a building to be truly passive, all of them must be used. As you will see, they often complement each other, and some simply do not "work" if not combined with others. These principles are orientation/azimuth, overhangs/shading, windows, insulation/air sealing, and thermal mass. Please read through the following descriptions of passive solar design and some passive solar design principles. Note that I provide a link as well as a .pdf since the links are archived and don't always work. All of the readings are from the California Energy Commission.
Please read through the following descriptions of passive solar design and some passive solar design principles. Note that I provide a link as well as a .pdf since the links are archived and don't always work. All of the readings are from the California Energy Commission.
Please read the following for some additional insight into thermal mass, which is essential for passive design but is not often used.
The foolwing provides a brief summary of these principles:
Generally speaking, most of these principles are easy to understand. It's all but common sense that you need good insulation and air sealing for an efficient home, and understanding that good orientation is important is easy to understand if you know that the sun is usually in the south in the northern hemisphere. We all know that windows allow sunlight in. There is some subtlety and basic trigonometry (uh oh) to overhangs, since you must consider sun angle at your latitude for proper design, so that can be a little tricky. But the fact that deciduous trees lose their leaves once a year is common knowledge. Thermal mass is the least commonly understood, but the basics are not difficult to understand (things that heat up slowly and release heat slowly). It bears repeating that for a fully passive solar design, all of these elements must be present and work in conjunction. As noted above, this almost certainly must be considered in the design process, since the building's orientation cannot be changed after it is built and some overhangs are difficult to retrofit. Windows, air sealing, insulation, and possibly thremal mass can generally be added after it is built, though.
Here is an example of a modern home that uses some passive design principles. See if you can find examples of using orientation, windows, shading, insulation, and air sealing.
Passive solar design refers to taking advantage of ambient daily and seasonal sunlight (or lack thereof) to heat and cool a building. Passive design in a more general sense includes any measure that reduces energy use by taking advantage of local conditions. Natural ventilation is one way to do this, as the video below details.
Note the use of prevailing breezes, orientation, and windows to help passively cool a home.
One final note about passive design before we move on: In case you think that these principles represent some modern breakthrough in knowledge, well, you are off by a few thousand years! Many ancient and historic civilizations all over the world not only understood these principles, but deployed them on a wide scale.
Please read through the following descriptions of how passive design has been used for thousands of years.
There is a saying that "if you want to pay attention to something, you need to measure it." As you are hopefully aware, there are many ways that buildings and urban/suburban development impact sustainability, e.g. through energy use, natural resource use, waste generation, impact on ecosystems, impact on biodiversity, impacts on pollution, and more. If we want to minimize these impacts and to be more sustainable, we need to figure out a way to measure these impacts. Enter green building ratings systems, aka green building metrics. There are too many ratings sytems to fully cover here, but the following provides some insight into some of the more common ones, as well as some that are less common.
Take a minute or two to think about the following (feel free to write down your answers): If you wanted to compare how sustainable one building is compared to another building, what would you look for? Think of specific things that 1) impact sustainability and 2) can be measured.
In the 1990s, the U.S. Green Building Council [161] (USGBC) undertook the same exercise. The result of this was Leadership in Energy and Environmental Design (LEED). LEED was the first widely-accepted "green" building rating system, and is now recognized worldwide. (Side note: the USGBC is a non-profit organization that provides an incredible amount of resources related to sustainable builiding design, many of them freely available. See their Courses and Events [162] site for details. There are also many local chapters [163] that host events.)
LEED is one of the most commonly recognized and used green building ratings systems in the U.S. and the world. You have almost certainly seen a LEED building, even if you did not know it was certified. Please read and watch the following summaries of how LEED "works."
As you can see, LEED is a points-based rating system. Remember all of those aspects of sustainable buildings you listed at the beginning of this page? LEED almost certainly provides "points" for each one of them. On a basic level, a building gets a specific amount of points for sustainable physical features such as water reduction, energy efficiency, renewable energy, use of native plants, use of local materials, use of non-toxic materials, and more subtle ones such as promoting public transportation, providing bike infrastructure, and designing the building to be used as an educational tool. Afte the building is designed and tested, the building achieves a certification level based on the points earned:
There are more complexities to actually getting certification, e.g. the the builiding owner works with a LEED professional and registers with USGBC from the outset, etc., but that goes beyond the scope of this course. There are also a number of different types of certifications, from single new buildings to interior design to operations and maintenance and more. More information on these is here [165]. If you are interested in reading more about the full LEED process, you can dig into the details here [166]. Note that there are job and training opportunities in this process. For more information see their Credentials [167]site.
Here is one example of a LEED building. Note the variety of sustainable features it has, from water to waste to energy and more. If you are so inclined, you can browse for LEED projects on the U.S. Green Building Council [168] website, including with a searchable database.
OPTIONAL - You can play around with the LEED for Homes checklist here [169], and access other checklists here [170].
One of the common critiques of LEED is that building owners/designers are not required to check all of the boxes (literally, in this case). In other words, it is possible to have a LEED building that overuses water, does not provide 100% of it's own energy, does not use entirely non-toxic or local resources, and so forth. You can pick and choose what you want to address, and the only penalty is that you might not get the certification level that you wanted. In addition, a building receives its LEED rating before the building is used. This can be a problem if the folks using the building do not operate it in such a way that the LEED goals are accomplished. For example, if the building has high levels of insulation and air sealing but the building occupants turn the thermostat up too high or low, or leave windows open, etc., then the building may use much more energy than the design claims.
The Living Building Challenge seeks to address these points, but more importantly it seeks to be the most robust and holistic sustainable building rating system available.
The Living Building Challenge is overseen by the Living Future Institute. Their goal is to "move beyond merely being less bad and to become truly regenerative." Based on personal experience and extensive research, Living Building Certification is indeed the most robust and holistically sustainable building rating system available today.
Please read and watch the following introductions from the International Living Future Institute. They provide a good overview of the intent and philosophy behind Living Buildings.
As you read [171]and saw, the core questions asked by the International Living Future Institute (ILFI) are:
It is important to take a minute to think about the implications of the first question in particular. The goal of ILFI goes beyond simply not making things worse in terms of sustainability to actually making things better by building buildings. The intent is summarized when they say: “Nothing less than a sea change in building, infrastructure and community design is required. Indeed, this focus needs to be the great work of our generation. We must remake our cities, towns, neighborhoods, homes and offices, and all the spaces and infrastructure in between. This is part of the necessary process of reinventing our relationship with the natural world and each other—reestablishing ourselves as not separate from, but part of nature, ‘because the living environment is what really sustains us.’” The Living Building Challenge is nothing if not ambitious!
The Living Building Challenge has seven (7) "petals" for certification. Each petal represents a different category of sustainability:
There are twenty (20) total "imperatives" within these petals. Each imperative has a specific, measurable standard that must be met in order to receive certification.
Among the standards required are:
As you can see, there are a few things that separate Living Buildings from LEED (and other) sustainable building metrics. The list is long, but primary among them are the following "Principles that govern the standard":
As a result of this being such a robust standard (and the fact that it must be used for a year prior to certification), there are only 30 fully certified Living Buildings [177] in the world, as compared to thousands of LEED buildings.
The following provides a description of a Living Building. As of 2018, this was only the second one in existence.
LEED and Living Buildings are holistic rating systems. There are a number or energy-only rating systems in the U.S. The following is a sampling of a few of them.
Energy Use Index (EUI) and Benchmarking are very common metrics in the energy management industry and energy policy world. They focus solely on energy use, and are relatively simple ways to assess and influence the energy efficiency of buildings.
First, read the following short reading about Energy Use Index (sometimes called "Energy Use Intensity") and watch the video below.
Benchmarking is a common practice in the commercial energy efficiency industry. The most commonly used software for this is Portfolio Manager from the U.S. Environmental Protection Agency (EPA). Read the summary of both of these below
An energy use index (EUI) is relatively easy to determine. You just take a year's worth of energy bills, convert the total energy use to kBTU (thousands of BTUs), then divide by square footage. That's it! This gives you a snapshot of the general energy efficiency of a building, though not a comprehensive one. It is a helpful basis of comparison for other buildings, which is exactly what EPA Portfolio Manager does. Portfolio Manager compares your building's EUI with other similar buildings. What is meant by "similar?" Well, that depends on a few factors, but the most important aspects are 1) buildings in a similar climate zone and 2) buildings that are used for similar things. For example, the mean EUI of an education building in the U.S. is 51 kBTU/ft2, while the mean EUI of a hospital is about 188 kBTU/ft2 (source: Lawrence Berkley National Laboratory Buildings Performance Database [180]). Why the difference? Think about the difference in operating hours and equipment used in these buildings. Given this, it would be unfair to compare the "typical" energy use of a hospital with the "typcial" energy use of a college or middle school. Similarly, you would expect slightly different energy use based on the climate. The exact same building in a temperate climate such as, say, Coastal North Carolina would use less energy than one in a cold climate such as Minnesota or Maine or a hot, humid climate such as Florida.
EPA provides you with an "Energy Score" based on other buildings in their database. A score of 25 means you have a lower EUI than 25% of comparable buildings, a score of 50 means you have a lower EUI than 50% and higher than 50%; a 90 means you have a lower EUI than 90% of buildilngs, and so on. EPA provides the option of being Energy Star rated if you have a score of 75 or above. Some municipalities (such as Philadelphia [181]) require buildings to obtain their Energy Score every year so that they may constantly see how they compare to other buildings. The benefit of doing this every year is that you are forced to keep up with your peer buililngs. Let's say you get a score of 75, then think: "Cool, I'm very efficient. I don't need to make any upgrades." But then if other buildings become more efficient over time, your score will drop. In this way, the process of improving efficiency in theory never ends.
Energy Star is a program created and run by the U.S. Environmental Protection Agency (EPA). As the name implies, this is an energy efficiency rating system that has the following four components:
a high efficiency thermal enclosure system (thermal envelope!)
According to the EPA [182], Energy Star certified homes "are at least 10% more efficient than homes built to code and achieve a 20% improvement on average." Please read the following summary of the Energy Star Residential New Construction Program:
Here is a great video that introduces some of the benefits of Energy Star Homes. It is geared towards builders but is a helpful introduction for anyone.
OPTIONAL
Passive House Certification is effectively a more robust version of Energy Star Certification. There are actually two different certifying bodies in the U.S. - Passive House Institute (PHI) and Passive House Institute U.S. (PHIUS) - as detailed by ecohome here [185]. The distinction is not important for our purposes, but we will focus on PHIUS standards. The image below provides a sense of how robust Passive House standards are relative to Energy Star and other standards. See this [186] document for a fuller explanation.
Please read the overview below and click on the second link to look at some of the differences between PHIUS and other energy efficiency standards:
The following is a summary of the energy-only rating systems:
Benchmarking:
Energy Star Certification
Passive House Certification
Finally, let's go over a few other sustainable building types and techniques. Tiny homes have been gaining in popularity for over a decade now (there are multiple shows and documentaries dedicated strictly to tiny homes, for example), mostly as a solution to exponentially increasing housing prices. But there is an element of sustainabiliy and freedom (e.g. "van life") to a tiny house as well, and many people are simply tired of the overconsumptive American lifestyle. We will also briefly go over a few less common examples, including straw bale, cob, earth bags, and cooperative housing.
Straw bale, Cob, and earth bags are much less common than most of the examples on previous pages, but are perhaps the most sustainable in terms of materials use since most of the structure is made from natural and local materials - mud, straw, gravel, and/or soil.Straw bale also provides excellent insulating value, and as you will see in the video below, cob is a good thermal mass and can be made into almost any shape.
Please read the following for an overview of each of these, then watch the video that provides details of a cob/straw bale hybrid house. in the video, note also all of the passive design principles that are used!
There is no single definition of cooperative housing, but at a fundamental level refers to housing that is co-owned and co-managed by a group of people. There are many different kinds of cooperative housing, and it has been practiced for thousands of years. In a Western context, cooperative housing usually refers to intentional communities that cooperatively own and manage a building and share resources and spaces. The following provides a good intro to some of the key ideals behind most cooperative housing.
Finally, tiny homes! Tiny homes were a niche application but have become much more mainstream now. They are small (usually less than 500 ft2), but relatively inexpensive ($10,000 - $100,000, depending on how fancy), and most of them are on wheels and so can be moved seasonally and avoid some permitting issues due to not having a foundation.
Here is a nice introductory video to tiny homes.
Here is one interesting application for tiny homes that helps address homelessness and substance abuse issues in Colorado.
I have visited and toured a number of cooperative buildings in Switzerland. Feel free to take a look at the pictures below for some insight into what they look like and how they operate. Note that there is no single set of rules for cooperative housing. The examples below only describe the ones that I saw in Switzerland. That stated, the types of rules at these Swiss examples are fairly typical for cooperative housing in that they are meant to foster low-impact, community-oriented living. One aspect that all cooperative housing shares in common is that the buildings are owned and managed cooperatively. All of the buildings below are owned by all occupants, including any businesses. All photos are my own.
Here are some more site visits! Again, this is not required reading. I suggest browsing through them if/when you have time. This may help inspire your final project proposals!
By now you should be able to do all of the following:
You have reached the end of Lesson 9! Double-check the to-do list on the Lesson Overview page [193] to make sure you have completed all of the activities listed there before you begin Lesson 6.
In the final full lesson of this course, you will learn some basics of Colorado geography (and geology), energy, energy policy, water, and water policy.
By the end of this lesson, you should be able to:
To Read | Lesson 6 Online Content | You're here! |
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If you have any general course questions, please post them to our HAVE A QUESTION discussion forum located under the Discussions tab in Canvas. I will check that discussion forum regularly to respond as appropriate. While you are there, feel free to post your own responses and comments if you are able to help out a classmate. If you have a question but would like to remain anonymous to the other students, email me through Canvas.
If you have something related to the material that you'd like to share, feel free to post to the Coffee Shop forum, also under the Discussions tab in Canvas.
Colorado is known as the "Centennial State" and is the 8th largest state [195] in the U.S. by area, at a little over 104,000 square miles. As a point of reference, it is over twice the size of Pennsylvania. However, it has only the 21st highest population [196], at just over 5.6 million people as of 2018. (Pennsylvania is 5th at around 12.8 million people.) The capital is Denver, which is known as the "Mile High City" because most of the city is at or above 1 mile above sea level. While known for its mountains, a significant portion of Colorado is part of the Great Plains and is nearly flat. Even the plains are at a high elevation, and in fact, Colorado has the highest average elevation of any state in the U.S. Colorado has more peaks higher than 14,000 feet (58 of them!) [197] than any state in the country. If you travel to Colorado for any amount of time, you will no doubt overhear discussions about these "fourteeners." It is nearly a universal pastime to climb fourteeners.
As you will read below, Colorado has a very diverse landscape and culture. It is known for the availability of outdoor activities (hiking, skiing, camping, white water rafting, biking, etc.), but also has an interesting mixture of modern and historic culture and practices. Farming and ranching are important to its economy and culture, but so are tourism, higher education, and high tech industries, among many other things. It is a wonderful state to explore!
As you probably recall, we will spend most of our time in Denver, but will also visit Boulder and drive through the mountains to the Western Slope towns of Paonia and Ouray (pronouned "ooh-ray"). We will thus experience a variety of Colorado culture and scenery, from the Eastern Plains to the Front Range, as well as the Western Slope. More details on these regions below.
Colorado has many local regions and other geographic features [200], but the major ones that we will experience are as follows:
See the video below the image for a good explanation of how the Rocky Mountains and the Front Range formed. Note the explanation of why Red Rocks and other parts of the Front Range are sedimentary rocks (made from ancient sediments such as sand and silt) that were originally layered on top of the granite "basement" rock, and the Rocky Mountains themselves are made of granite that was pushed up via oceanic subduction. Some of this granite core is over 1 billion years old! (Side note: Geology is awesome!)
Please read the following sections of this article from Encyclopaedia Britannica [207]:
Another well-known feature of the state is the Continental Divide, sometimes referred to as the Great Divide. A continental divide is defined by National Geographic [208] as "a naturally occurring boundary or ridge separating a continent’s river systems. Each river system feeds into a distinct ocean basin, bay, or sea." As you can see in the image below, there are a number of continental divides in North America. Each of these lines is the boundary between two major drainage basins. The rivers and streams in each basin lead to a specific large body of water.
For example, the Eastern Continental Divide runs through Pennsylvania. Flowing water to the east of the divide ends up in the Atlantic Ocean, and west of the divide ends up in the Gulf of Mexico. In Colorado, water to the west of the Continental Divide flows to the Pacific Ocean, and to the east flows to the Gulf of Mexico (and ultimately the Atlantic Ocean). You may see signs while traveling through the mountains of Colorado like the one below that mark portions of the Continental Divide. There is also a trail that roughly follows the divide that is a national park - Continental Divide National Scenic Trail [209].
As the saying goes: "Whiskey's for drinking, water is for fighting." This is not far from the truth in Colorado! Water use and water rights are prominent issues in the state. It is an unusual experience for anyone that grew up on or near the East Coast, where the issue of water rights almost never comes up, to move to Colorado and find out that the "average" person is conversant in water rights. Water is such an important issue for Coloradans (and many who live in the western United States) because it is relatively scarce. As you can see in the maps below, most of the state receives under 20 inches of precipitation per year, and in fact, the average rainfall across the state is 15 inches per year, according to Denver Water [214]. This makes most of the state semi-arid, which means that it is climatologically not far away from a desert (arid) environment. As a point of comparison, most of the land east of the Mississippi receives more than 35 inches per year, with State College, PA receiving about 40 inches per year [215].
Further complicating matters is the comparison of the rainfall and population geographies of the state. Recall that the Western Slope of Colorado lies west of the Continental Divide and the Eastern Slope (including the Front Range) to the east. According to "Water Law" (Denver Water) [214], 10 percent of the state's residents live on the Western slope, but it contains 33 percent of the state's land and 70 percent of its water. Because of this, Western Slope water is often used on the Eastern Slope. This, in addition to relative scarcity and Colorado water laws, has contributed to water being a major issue in the state.
Please read the following summary of Denver and Colorado water policy. Read the sections entitled "Water law," "Water rights," "Rain barrels," and "Graywater use."
Colorado has a very diverse and often contentious energy landscape. For example:
While traveling through Colorado, it is not uncommon to see oil pump jacks, wind turbines/farms, fracking operations, solar arrays, and coal-fired power plants. (We will probably see more than a few of each during our time there.) Solar Energy International [48] has its training headquarters in Paonia on the Western Slope (we will visit them), yet fracking wells dot the local landscape and it is not uncommon to see train cars full of coal while traveling to and from Paonia. This variety can and does cause conflict, with fossil fuel advocates having strong disagreements with renewable energy advocates on personal and political levels.
The image below shows Colorado's 2019 fuel mix (the latest data available). You have seen this type of chart in EM SC 240N. Remember that this is called a "Sankey" chart and indicates energy flows. The numbers are all Trillions of BTUs (TBTUs) of energy, and the lines indicate the energy flows to different sectors. Remember that you read the chart from left to right, and can follow each primary energy source (the sources to the left) to see where they are used.
Energy policy can be very intricate and can vary significantly from state-to-state and even within states. If you are interested in finding out which energy policies exist in each state (and nationally), hands-down the best website for details is DSIRE [225], which is out of NC State University but is managed in conjunction with the U.S. Department of Energy. Believe it or not, DSIRE lists 133 energy policies [226] that apply to the state of Colorado! (Note that some of these are federal policies that apply in all states.) Obviously, we do not have time to go over all of them, but a few of the most prominent ones are below.
Renewable Portfolio Standards (RPSs) are created through legislation and require electricity providers to provide a certain percentage of their electricity from renewable (or alternative) sources. Each state is able to pass its own RPS law (or not), as there is no national RPS in the U.S. Each RPS dictates the percent targets compliance years (see below), and also indicates which energy sources can be used to meet the RPS goal.
Utilities must prove that the required percentage of the electricity they sell is from one of the eligible renewable sources. The three primary ways they do this is a) build and generate their own renewable electricity installations (e.g. a large solar array or wind farm), b) purchase renewable energy from a dedicated supplier (e.g. an independent owner of a large solar array or wind farm), or c) "take credit" for renewable electricity generated by customers on their grid. Utilities rarely build their own generation facilities nowadays (option a), but signing long-term contracts with independent suppliers is becoming very common (option b).
It is very common for utilities to "take credit" for customer-generated electricity, in particular through residential solar arrays. They do this by paying the customer a fee to take credit for the electricity they generate. Each credit is called a "renewable energy credit (or certificate)" (REC), though solar credits are often referred to as SRECs (solar renewable energy credits). REC and SREC prices are set by different mechanisms, but usually, they are sold on the open market. There are too many details to go into here, but here is an example of how this could work: Let's say I have a solar array and I generate 1,000 kWh of electricity in a year (this is 1 MWh of electricity). If the utility agrees to pay $50/SREC, then they would pay me an additional $50 at the end of the year. If I generate 2 MWh, I would get $100, and so on. This is in addition to me not having to pay for the electricity that I generate! In other words, if I generate 1,000 kWh, that is 1,000 fewer kWh that I have to pay the utility for. (This is referred to as net metering.)
RPS benchmarks gradually increase, e.g. 5% in year one, 7.5% in year two, and so on. If a utility does not meet the benchmark in a given year, they are penalized (usually fined).
For example, Colorado passed an RPS in 2004. Details can be found here [227]. Some details relevant to the discussion above are as follows:
A tax credit is just that, a credit. When an individual or business investor earns a tax credit it means that the amount of the credit will be subtracted from a future tax bill. In the United States, we have a Federal Residential Renewable Energy Tax Credit [229] which provides a tax credit covering 26% of the cost of installation. This is commonly referred to as the investment tax credit or ITC. If you put a photovoltaic system on your roof at a cost of $30,000, you earn a $7,800 tax credit. The government doesn’t mail you a check for this amount. It means you get to deduct that amount from your next tax payment. To realize this money, you will need to have paid at least $9,000 in taxes, but excess credits can "generally" be carried over to future tax years. Note that even if you were owed a refund, this tax credit can be used to increase your refund, as long as you paid at least $7,800 in federal income tax throughout the year. Eligible energy sources include "solar water heat, solar photovoltaics, geothermal heat pumps, wind (small), [and] fuel cells using renewable fuels." This is only applicable to residential customers.
Essentially the same ITC (but it is technically the Business Energy Investment Tax Credit [230]) applies to corporate owners in the following sectors "commercial, industrial, investor-owned utility, cooperative utilities, and agricultural." So basically everyone except for residential, and non-profits. The incentive levels are a little different for some of the energy sources, but solar, wind, and fuel cells earn a 26% credit in 2021, which then decreases at the same rate as the residential ITC afterward.
A production tax credit (PTC) [231] provides an incentive for each kWh of renewable electricity generated and is not based on the up-front cost of the technology. This is a federal incentive. Well, was, anyway. It expired at the end of 2021. This is a per kWh incentive applied to specific installations that were completed prior to the expiration date. The incentives last for 10 years. For example, there was a $0.015/kWh incentive for wind installations prior to 2022. This may not seem like much, but adds up over 10 years! For example, a 2 MW turbine with a 40% capacity factor would generate the following revenue:
A 2 MW turbine is actually on the smaller end of new wind turbine sizes, so even a seemingly meager PTC can be a big deal!
Again, these are only a few of the many, many energy policies that apply to the State of Colorado! This will help provide some context for our experience there, and knowing where to access energy policy information will be helpful for your projects.
By now you should be able to do the following:
You have reached the end of Lesson 6! Double-check the to-do list on the Lesson 6 Overview page [232] to make sure you have completed all of the activities listed there before you move on to the next lesson.
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[227] http://programs.dsireusa.org/system/program/detail/133
[228] http://ncsolarcen-prod.s3.amazonaws.com/wp-content/uploads/2018/10/Renewable-Portfolio-Standards-2018.pdf
[229] https://programs.dsireusa.org/system/program/detail/1235/residential-renewable-energy-tax-credit
[230] http://programs.dsireusa.org/system/program/detail/658
[231] http://programs.dsireusa.org/system/program/detail/734
[232] https://www.e-education.psu.edu/emsc297/696