Comparison of frequency distribution of plant life-forms (based on [11]).
\r\n\t
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Dr. Tiefenbacher has published more than 200 papers on a diverse array of topics that examine perception and behaviors with regards to the application of pesticides, releases of toxic chemicals, environments of the U.S.-Mexico borderlands, wildlife hazards, and the geography of wine.",coeditorOneBiosketch:null,coeditorTwoBiosketch:null,coeditorThreeBiosketch:null,coeditorFourBiosketch:null,coeditorFiveBiosketch:null,editors:[{id:"73876",title:"Dr.",name:"John P.",middleName:null,surname:"Tiefenbacher",slug:"john-p.-tiefenbacher",fullName:"John P. Tiefenbacher",profilePictureURL:"https://mts.intechopen.com/storage/users/73876/images/system/73876.jfif",biography:"Dr. John P. Tiefenbacher (Ph.D., Rutgers, 1992) is a professor of Geography at Texas State University. His research has focused on various aspects of hazards and environmental management. Dr. Tiefenbacher has published on a diverse array of topics that examine perception and behaviors with regards to the application of pesticides, releases of toxic chemicals, environments of the U.S.-Mexico borderlands, wildlife hazards, and the geography of wine. More recently his work pertains to spatial adaptation to climate change, spatial responses in wine growing regions to climate change, the geographies of viticulture and wine, artificial intelligence and machine learning to predict patterns of natural processes and hazards, historical ethnic enclaves in American cities and regions, and environmental adaptations of 19th century European immigrants to North America's landscapes.",institutionString:"Texas State University",position:null,outsideEditionCount:0,totalCites:0,totalAuthoredChapters:"1",totalChapterViews:"0",totalEditedBooks:"6",institution:{name:"Texas State University",institutionURL:null,country:{name:"United States of America"}}}],coeditorOne:null,coeditorTwo:null,coeditorThree:null,coeditorFour:null,coeditorFive:null,topics:[{id:"12",title:"Environmental Sciences",slug:"environmental-sciences"}],chapters:null,productType:{id:"1",title:"Edited Volume",chapterContentType:"chapter",authoredCaption:"Edited by"},personalPublishingAssistant:{id:"194667",firstName:"Marijana",lastName:"Francetic",middleName:null,title:"Ms.",imageUrl:"https://mts.intechopen.com/storage/users/194667/images/4752_n.jpg",email:"marijana@intechopen.com",biography:"As an Author Service Manager my responsibilities include monitoring and facilitating all publishing activities for authors and editors. From chapter submission and review, to approval and revision, copyediting and design, until final publication, I work closely with authors and editors to ensure a simple and easy publishing process. I maintain constant and effective communication with authors, editors and reviewers, which allows for a level of personal support that enables contributors to fully commit and concentrate on the chapters they are writing, editing, or reviewing. I assist authors in the preparation of their full chapter submissions and track important deadlines and ensure they are met. I help to coordinate internal processes such as linguistic review, and monitor the technical aspects of the process. As an ASM I am also involved in the acquisition of editors. 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Venkateswarlu",coverURL:"https://cdn.intechopen.com/books/images_new/371.jpg",editedByType:"Edited by",editors:[{id:"58592",title:"Dr.",name:"Arun",surname:"Shanker",slug:"arun-shanker",fullName:"Arun Shanker"}],productType:{id:"1",chapterContentType:"chapter",authoredCaption:"Edited by"}},{type:"book",id:"878",title:"Phytochemicals",subtitle:"A Global Perspective of Their Role in Nutrition and Health",isOpenForSubmission:!1,hash:"ec77671f63975ef2d16192897deb6835",slug:"phytochemicals-a-global-perspective-of-their-role-in-nutrition-and-health",bookSignature:"Venketeshwer Rao",coverURL:"https://cdn.intechopen.com/books/images_new/878.jpg",editedByType:"Edited by",editors:[{id:"82663",title:"Dr.",name:"Venketeshwer",surname:"Rao",slug:"venketeshwer-rao",fullName:"Venketeshwer Rao"}],productType:{id:"1",chapterContentType:"chapter",authoredCaption:"Edited by"}},{type:"book",id:"4816",title:"Face Recognition",subtitle:null,isOpenForSubmission:!1,hash:"146063b5359146b7718ea86bad47c8eb",slug:"face_recognition",bookSignature:"Kresimir Delac and Mislav Grgic",coverURL:"https://cdn.intechopen.com/books/images_new/4816.jpg",editedByType:"Edited by",editors:[{id:"528",title:"Dr.",name:"Kresimir",surname:"Delac",slug:"kresimir-delac",fullName:"Kresimir Delac"}],productType:{id:"1",chapterContentType:"chapter",authoredCaption:"Edited by"}},{type:"book",id:"3621",title:"Silver Nanoparticles",subtitle:null,isOpenForSubmission:!1,hash:null,slug:"silver-nanoparticles",bookSignature:"David Pozo Perez",coverURL:"https://cdn.intechopen.com/books/images_new/3621.jpg",editedByType:"Edited by",editors:[{id:"6667",title:"Dr.",name:"David",surname:"Pozo",slug:"david-pozo",fullName:"David Pozo"}],productType:{id:"1",chapterContentType:"chapter",authoredCaption:"Edited by"}}]},chapter:{item:{type:"chapter",id:"62006",title:"Introductory Chapter: Global Aspects and Scientific Importance of Desert Ecological Research",doi:"10.5772/intechopen.78368",slug:"introductory-chapter-global-aspects-and-scientific-importance-of-desert-ecological-research",body:'\nIf ecologists or environmental scientists are talking about desert ecological research, then almost everyone is thinking about specific desert flora [1, 2, 3, 4, 5], fauna [6, 7], or desertification itself as a consequence of climate change [8, 9], or sand dunes-triggered disasters [10]. In fact, the importance of ecological research in deserts is far more general and wider. For deeper understanding of this importance need to overview the definition of deserts from different viewpoints, the real areas of deserts, and some basic production biological data.
\nEfficient functioning of the Earth’s ecosystems is based on the autotrophic plant life, which can make use of the radiation energy of the Sun directly. This plant life needs, besides the light of the Sun, simultaneous availability of minerals in the lithosphere, carbon dioxide in the atmosphere, and liquid water in the hydrosphere. Thus, biosphere appears on the interface of these three spheres. Where these four factors are available in the most efficiently usable form, tropical rainforests can be found. Every other habitat is more or less a “struggle zone” for plants because some of the four above mentioned factors limit the biosphere. Based on the degree of environmental limitations, ecosystems can be arranged along a scale. Desert ecosystems can be found on the opposite endpoint of this scale compared to tropical rainforests. Semi-deserts can be found near deserts on this imaginary line, just a little bit nearer the other endpoint of the scale.
\nIf this most general definition of deserts is accepted, several habitats, which are not referred to as deserts in the habitual language use must be considered to be deserts. In order to quantify the scale, we can use biomass per area as a static indicator as well as net primary production per area per time as a dynamic indicator. Biomass of tropical rainforests is characterized by 2200 g/m2/year net primary production (NPP) and 45,000 g/m2 biomass, this is currently the “ideal existence status” of the biosphere. In the case of deserts, NPP is between 0 and 3 g/m2/year and biomass is between 0 and 20 g/m2. In the case of semi-deserts, NPP amounts to 3–150 g/m2/year and biomass amount to 20–700 g/m2.
\nDesert or semi-desert conditions can be caused by:
Lack of liquid water usable for plants (arid areas without precipitation)
areas without precipitation (orographical, e.g., Gobi, Tibet, or cool, dry deserts, e.g., Namib, Atacama)
areas with much larger evapotranspiration than precipitation due to the heat (southern and central part of Sahara)
permanently frozen areas (Greenland, Antarctica, and peaks of high-altitude mountains)
sheer, unweathered rock surfaces where water runs off (barren, rocky areas in mountains)
Lack of access to minerals in the lithosphere
Photic zone of open oceans (where biomass has a desert value of only 3 g/m2, which is even less than that in the Sahara, however, NPP has a semi-desert value of 125 g/m2/year)
Lack of light
Abyssal water of open oceans, caves (special ecosystem with low productivity)
Lack of air and light
Inner part of the rock masses of the Earth (where microbial life may often exist)
Continuous physical disturbance, which prevents plants from settling in
Coastal tidal zone
Fast-running reaches of rivers
Shifting sand areas
Volcanic areas exposed to regular lava flow or tuff eruption
Areas exposed to anthropogenic transformation and disturbance (urban concrete surfaces, airports, highways—“anthropogenic deserts”)
Areas exposed to extreme environmental pollution (e.g., mazut lakes)
Certain agricultural areas with low productivity (not irrigated, plowed areas with regular disturbance, lying fallow most of the year, semi-desert category in annual average)
At the borders of the semi-desert category, there are tundra, open grasslands (e.g., rocky, saline, and mountain) and several other habitat types besides classic tropical and temperate semi-deserts.
\nVegetation is normally able to evapotranspirate water equivalent to 20 mm of precipitation at a temperature of 10°C. A month is considered to be climatically arid if its monthly average temperature exceeds double the monthly amount of precipitation. If each of the 12 months of the year is arid in multi-year average, the area is considered to be a desert from a climatic point of view. If less than 2 months of the year are not arid, we speak about semi-desert climate. Similarly, if the multi-year average of the monthly average temperatures is below 0°C for 12 months, we speak about ice desert from a climatic point of view; if the period with an average temperature above 0°C lasts up to 2 months, the climate is tundra. However, the climatic approach may be misleading because the typical vegetation type of a certain area does not depend on the climate only.
\nPlants and animals have been able to adapt to areas with different environmental (among them climatic) conditions better and better during the evolution (on a historic time scale). In the second part of the Cambrian period (approx. 542–488 million years ago), hot tropical conditions were dominating most of the Earth, however, 100% of land could be considered a desert, only traces of some coastal invertebrates indicate terrestrial life. Also, during the Ordovician (488–443 million years ago), the climate was hot in several areas, the first plants (liver mosses and hyphae) appeared on land, however, this type of vegetation could have reached rather desert than semi-desert level. The first vascular terrestrial plants appeared in the Silurian (443–416 million years ago), however, they began to form vegetation mainly on the waterside, the continents’ interior kept being a desert for the most part from a vegetation point of view. During the evolution of terrestrial life, more and more various adaptation modes have appeared in response to the various climatic conditions, and this process is still going on. At the same time, climatic regulation capacity and generally self-regulation capacity, biodiversity, total biomass, and productivity of the biosphere have also shown an increasing tendency (excluding fall-backs caused by climatic variation).
\nVegetation types have reached various levels regarding adaptation to the abiotic conditions of the given habitat, which is also shown by the distribution of plant life-forms. Long-living K-strategists and phanerophyte life-form are dominating where vegetation has been able to adapt efficiently to existing conditions. However, where the habitat is rather a “struggle zone”, shorter-living r-strategists, herbaceous annual, or rosette plants are dominant (see Table 1).
\n\n | Therophytes | \nCryptophytes | \nHemi-cryptophytes | \nChamaephytes | \nPhanerophytes | \nEpiphytes | \n
---|---|---|---|---|---|---|
Tropical rainforests | \n— | \n— | \n— | \n10–20% | \n60–80% | \n10–20% | \n
Tropical and temperate desert and semi-desert | \n40–50% | \n5–10% | \n10–20% | \n10–20% | \n5–10% | \n— | \n
Ice and tundra | \n1–5% | \n1–5% | \n60–70% | \n20–30% | \n— | \n— | \n
Comparison of frequency distribution of plant life-forms (based on [11]).
Thus, deserts and semi-deserts are “front lines” of the expansion of biosphere, and therefore, their research (similarly to tropical rainforests) is highly important regarding life and future of mankind.
\nGlobal ecological importance of deserts and semi-deserts in the broader sense can be estimated according to their area and indicators of their vegetation. Tropical rainforest can be a reference base as a counterpoint, however, when speaking about deserts and semi-deserts in the broader sense, tundra and artificial deserts (human-transformed areas) must be considered as well besides tropical and temperate deserts and semi-deserts in the narrower sense. Land takes up approximately 150 million km2 on Earth from which approximately 15 million km2 are covered with ice, mainly in Antarctica and Greenland. Table 2 shows potential and current values of tropical rainforests as well as areas considered as desert and semi-desert in the broader sense, excluding the before mentioned ice fields. Table 3 shows the sources of data. Comparison of habitat types can be based on carbon stock in the biomass (t/ha), yearly carbon sequestration by primary production (t/ha/year), and biodiversity of the habitat type (species number per 10,000 km2). These data can be found in Table 4 and their sources in Table 5.
\n\n | Africa km2 | \nSouth America km2 | \nNorth America km2 | \nAsia km2 | \nEurope km2 | \nPacific km2 | \nTotal km2 | \n
---|---|---|---|---|---|---|---|
Lowland rainforest | \n4.0177 × 106–8.7000 × 105 | \n7.0721 × 106–4.5400 × 106 | \n0 | \n3.4907 × 106–1.7700 × 106 | \n0 | \n0 | \n1.4581 × 107–7.8000 × 106 | \n
Deserts | \n1.7022 × 106–1.0932 × 106 | \n2.7405 × 106–8.7276 × 105 | \n2.2211 × 106–5.8855 × 105 | \n1.3390 × 107–6.7763 × 106 | \n0 | \n3.9828 × 106–3.6949 × 106 | \n3.9357 × 107–2.2865 × 107 | \n
Tundra | \n0 | \n0 | \n1.8922 × 106–1.8922 × 106 | \n1.8922 × 106–1.8922 × 106 | \n2.6542 × 105–2.6542 × 105 | \n0 | \n4.0497 × 106–4.0497 × 106 | \n
Human areas | \n1.4140 × 103–4.1679 × 104 | \n7.0490 × 103–1.4854 × 105 | \n2.5700 × 102–1.8185 × 105 | \n4.3900 × 102 − 3.8400 × 104 | \n4.4390 × 103 − 1.1406 × 105 | \n4.9000 × 101 − 1.3871 × 104 | \n1.3647 × 104 − 5.3840 × 105 | \n
Potential and current areas.
In the case of natural ecosystems, the first number shows the area before human interference, whereas the second one shows the remnant at the turn of the millennium. In the case of human areas, the first value refers to the 1700s, whereas the second one refers to the turn of the millennium.
\n | Africa | \nAsia | \nNorth America | \nSouth America | \nEurope | \nPacific | \n
---|---|---|---|---|---|---|
Lowland rainforest | \nFRA ([12]) | \nFRA ([12]) | \nSee at South America | \nFRA ([12]) | \n— | \nSee at Asia | \n
Deserts | \nHannah et al. ([13]) | \nHannah et al. ([13]) | \nHannah et al. ([13]) | \nHannah et al. ([13]) | \n— | \nHannah et al. ([13]) | \n
Tundra | \n— | \nBrink ([14]); Tchebakova et al. ([15]); Golubyatnikov et al. ([16]) | \nBrink ([14]); Tchebakova et al. ([15]); Golubyatnikov et al. ([16]) | \n— | \nBrink ([14]); Tchebakova et al. ([15]); Golubyatnikov et al. ([16]) | \n— | \n
Human areas | \nGoldewijk et al. ([17]) | \nGoldewijk et al. ([17]) | \nGoldewijk et al. ([17]) | \nGoldewijk et al. ([17]) | \nGoldewijk et al. ([17]) | \nGoldewijk et al. ([17]) | \n
Sources of data shown in Table 2
\n | Carbon stock C t/ha | \nCarbon sequestration C t/ha/year | \nSpecies number/10,000 km2 | \n
---|---|---|---|
Lowland rainforest | \n210 | \n13–17 | \n2750 | \n
Deserts | \n3 | \n1.15–2.69 | \n457 | \n
Tundra | \n2.5 | \n1.94 | \n227 | \n
Human areas | \n5 | \n2.2 | \n1684 | \n
Carbon stock, carbon sequestration and species number per unit area.
\n | Carbon stock C t/ha | \nCarbon sequestration C t/ha/year | \nSpecies number | \n
---|---|---|---|
Lowland rainforest | \n\n | \nGirardin et al. ([18]) | \nBarthlott et al. ([19]) | \n
Deserts | \nMelillo et al. ([20]) | \nIto and Oikawa ([21]) | \nEllis et al. ([22]) | \n
Tundra | \nMelillo et al. ([20]) | \nIto and Oikawa ([21]) | \nEllis et al. ([22]) | \n
Human areas | \nMelillo et al. ([20]) | \nHaberl et al ([23]) | \nEllis et al. ([22]) | \n
Sources of carbon stock, carbon sequestration and species number per unit area values.
These habitats offer a wide range of ecosystem services, among others due to the climate regulation role of the assimilated and retained carbon stock. Monetary value of these is shown in Table 6, based on a price of $11 per ton (Interagency Working Group, 2013).
\n\n | Carbon stock | \nAssimilated carbon | \n||
---|---|---|---|---|
\n | $ on potential area | \n$ on current area | \n$ on potential area | \n$ on current area | \n
Lowland rainforest | \n1.23 × 1013 | \n3.76 × 1012 | \n7.64 × 1011–9.99 × 1011 | \n3.76 × 1011–4.92 × 1011 | \n
Deserts | \n4.76 × 1011 | \n2.77 × 1011 | \n1.83 × 1011–4.27 × 1011 | \n1.06 × 1011–2.48 × 1011 | \n
Tundra | \n4.08 × 1010 | \n4.08 × 1010 | \n3.17 × 1010 | \n3.17 × 1010 | \n
Alpine vegetation | \n5.76 × 1010 | \n2.95 × 1010 | \n2.41 × 1010 | \n1.23 × 1010 | \n
Urban area | \n2.75 × 108 | \n1.09 × 1010 | \n1.21 × 108 | \n4.78 × 109 | \n
Monetary value of carbon dioxide in $
Global problems of our time are basically human ecological ones with the interplay of environmental and social factors. The most important global crisis phenomena are closely connected with each other, form a coherent system, and are associated with the anthropogenic disorders of the healthy functioning of the biosphere.
\nMain crisis phenomena are:
Global overpopulation crisis (population explosion),
Global climate change,
Global biodiversity crisis (mass extinction of species, habitat loss, the collapse of ecosystems),
Global social crisis (income scissors opening wider),
Global information crisis (insufficiency of scientific synthesis, overspecialization, publication flood), and
Lack of global coordination (independent influence of 195 nation states without substantive common planning and regulation).
Several of these problems are linked to the ecological research of deserts. Among the anthropogenic causes of desertification, overpopulation plays an important role; however, this increases the global social crisis as feedback. Global climate change is a cause and a consequence at the same time, since draught results in desertification, however, low plant production decreases carbon sequestration, which further enhances climate change. This group of phenomena is apparently closely connected with the biodiversity crisis also as a cause and an effect. Global information crisis makes itself felt in this area as well, since new data and knowledge are increasing exponentially, see Figure 1. It shows the yearly number of international scientific articles with keywords desert + ecology in their abstracts according to the Scopus database, for the period 1912–2018 (downloaded on April 18, 2018, thus data for 2018 are quarterly ones).
\nNumber of articles with keywords desert + ecology in their abstracts in the Scopus database (downloaded on April 18, 2018).
When examining the genre of these publication data (rate of document types, Figure 2), one can see that 90.7% of the publications are made up of primary publications (journal articles) and pre-publication (conference papers), and only 7.4% of them is synthesis (review articles, book chapters, or books). Thus, new information is produced much faster than we can organize it into a system of thought.
\nDistribution of articles with keywords desert + ecology in their abstracts according to a document type in the Scopus database (downloaded on April 18, 2018).
Solving global problems (among them desertification problems) of mankind is mainly hindered by the lack of global coordination, which would serve the protection of the common interest and align the efforts of mankind. Solving global problems needs efficient international cooperation, aligned scientific research, aligned political decision-making, legislation and economic regulation.
\nGlobal warming and climate change are rising issues during the last couple of decades. Buildings including commercial and residential ones are major contributors to energy consumption [1]. Energy consumption in buildings significantly increases on a yearly basis due to the increased human comfort needs and services [2]. Multiple factors affect the energy consumption used for cooling buildings such as wall structure, window to wall ratio, and building orientation in addition to weather conditions [3]. Energy consumed by buildings was reported to compose a relatively large proportion of the global energy consumption [4]. The building construction and the way it is operated and maintained have a significant impact on the total energy and water usage of the world resources [5].
Buildings are the primary energy consumers contributing to more than 40% of the US energy usage [6]. According to the US Department of Energy (DoE), the heating, ventilation, and air-conditioning (HVAC) systems consume approximately 17–20% of the total energy bill of any facility or building [7]. The world equipment demand for HVAC systems has increased worldwide from approximately 50 billion US dollars in 2004 to more than 90 billion US dollars in 2014 and for the United States from almost 11 billion to 19 billion US dollars over the same period [8].
Thermal characteristics of building envelopes have become of rising significance for designers and owners due to its relation to energy consumption reduction. Improper thermal insulations in buildings can lead to higher chances of surface condensation when air has relative humidity higher than 80% and when the convective and radiative heat transfer coefficients of the exterior walls are small [9].
The purpose of this chapter is to discuss benefits and design guidelines for zero energy buildings. NZEBs have tremendous potential to transform the way buildings use energy. In response to regulatory mandates, federal government agencies and many other state and local governments are beginning to move toward targets for NZEBs.
Many states in the United States are mandating many rules and regulations to reduce the buildings’ energy consumption. For example, New York and California, which house more than 20% of the United States’ population, produce less than 10% of its carbon emissions [10]. These two states are leading the way in decreasing energy use through the proliferation of net-zero energy building in addition to other strategies.
According to the US Department of Energy (DoE), a zero-energy building was defined as the building that produces enough renewable energy to meet its own annual energy consumption requirements [11]. According to the European Union Article 2, a nearly zero-energy building is a building that has a very high energy performance where low energy is required by the building which should be covered to a very significant extent from renewable sources including sources produced on-site or nearby [12].
There are several metrics that define the performance of buildings such as the net-zero site energy building, net-zero source energy buildings, net-zero energy cost building, and net-zero energy emission building.
The net-zero site energy building is defined as the building that produces as much energy as it consumes when measured at the site. The net-zero source energy building is the building that produces as much energy on an annual basis as it uses as compared to the energy content at the source. On the other hand, the net-zero energy cost building is the building that uses energy efficiency and renewable energy strategies as part of the business model. Lastly, the net-zero energy emission buildings is the building design that looks at the emissions that were produced by the energy needs of the building. Figure 1 shows various energy efficiency measures.
Various energy efficiency measures.
In the last decade, energy costs have been rising, fuels are running out, and there have been global warming issues. For example, the United Kingdom has only 2 years of gas reserve, which has been put on hold of usage, and is currently buying from other countries such as Qatar and the United States. In addition to that, there have been many other issues such as health, well-being, and pollution which could be reduced if emissions are reduced as a result of better energy consumption plan.
Power stations convert only 30–35% of the input energy into electricity. The rest is rejected as waste heat. The United Kingdom alone wastes £20 billion each year by heat rejection from power plants which if used appropriately could heat Britain.
Earth’s source of fossil fuel is vanishing at a much rapid pace during the last 200 years causing high damage rates to climate change. New reserves of fossil fuels are becoming harder to find. Those that are discovered are significantly smaller than the ones that have been found in the past. Oil reserve is expected to vanish between 2050 and 2060 and so does that for gas. Coal will last longer and is expected to last till 2100 [13].
Other aspects of increased emissions and increased rate of energy consumption are global warming and significant increase rate of ice melting and glaciers. A prominent red flag out of these aspects is that nine of the ten warmest years since 1880 have been in the last decade [14]. For global warming concern, Miami has seen a temperature rise of 3°C.
A building that is designed to be more sustainable has the potential to reduce the human impact on the environment. This effect is shown in Figure 2.
Effect of sustainable buildings on the environment, social life, and economic development.
Sustainable development is the development that meets the present needs without compromising the ability of future generations to meet their own needs [15].
There are three pillars for sustainable development:
Environmental protection
Social concerns
Economic development
The environmental protection aspect deals with climate change issues, resource depletion, land use and ecology, and waste concerns and impact of cities. The human social concerns and issues deal with justice, intragenerational equity, intergenerational equity, and health and well-being issues. On the other hand, the economic development deals with developed and developing counties, employment, modernization, and technological changes.
To solve current issues toward sustainable designs, designers should meet most of the items listed under each of the three pillars. These could be visualized as the intersection common areas shown in Figure 3.
Designers’ choice to achieve the best results that meet sustainable designs.
Spreading knowledge and engagement are ultimately the top most factors to help in reducing energy consumption, pollution and emission, and other issues such as global warming. The process starts with engagement and knowledge spreading, but it should be a closed cycle and thus needs feedback on performance. There has to be supplies that provide low and zero carbon energy and, lastly, investment. With no commitment from big industrial countries, no progress would be achieved.
There are many organizations who started net-zero marketing and application such as environmental organizations, research centers, universities and schools, and some engineering solutions which aimed to save costs and energy. In the United States, California and New York are leading the way to net-zero designs. Although they occupy more than 20% of the total population in the United States, they contribute to less than 10% of the total pollution emissions.
Following design standards is the first step in the design to achieve a net-zero energy building as it is important to define the sources and inputs that would be necessary to quantify the outputs and check what it needs to balance the net-energy consumed. The next step is to simulate the energy consumption using various energy modeling techniques and tools to optimize the following:
Building orientation
Glazing area, exposure, and shading
Heat island reduction
Lighting systems and capacities
Temperatures, humidity, and relative humidity levels
Landscaping
Natural resources
The overall system efficiency
All factors should be considered together by employing passive heating or cooling strategies, such as solar chimney and direct heat gain through south-facing glazing and/or isolated gain or sunspace, considering all possible exterior wall construction that avoids thermal bridging and increasing the R-value in all roof construction, using efficient lighting system, utilizing daylighting sensors and occupancy sensors, and lastly using energy-efficient office equipment for commercial buildings and energy-efficient utilities for residential houses and buildings.
The designer should then implement life cycle analysis, net-zero water system, and net-zero energy and optimize the design as per occupancy levels.
There are three principles to achieve a good net-zero energy building design:
Building envelope measures
Not only the building should be oriented to minimize HVAC loads, but shades and overhangs should be used to reduce the direct sunrays. Multiple options are available such as roof overhangs, shades and awning, and vegetation. To reduce the heat gain through windows, the designer should avoid glazing on the east/west façade. Other measures to reduce heat gains are to increase insulation on opaque surfaces, use glazing with low solar heat gain coefficient values, use double-skin façade, and refine the building envelope to suit location conditions.
Energy efficiency measures
The first utmost factor is selecting the right-size systems for the building. This can be achieved by following ASHRAE Standard 90.1 safety factors in the design, applying factors to reasonable baseline cases, and using simulation to model the design and predict the optimized requirements. In the simulation, part load performance should be considered which would come useful when using variable volume systems, variable speed drives, variable capacity boilers, variable capacity chiller systems, and variable capacity pumping systems as well. In addition to this, the designer should consider using high-efficiency lighting and control systems such as LED lights, high-performance ballasts, dual circuited task lighting, occupancy sensors, and daylighting dimming sensors.
The designer should shift electric loads during peak demand which would optimize the energy consumption. Some recommendations for optimizing the HVAC loads are (1) using heat recovery chillers, (2) using underfloor air distribution systems, (3) using high-efficiency chillers, (4) using passive cooling, (5) applying thermal storage using phase-change materials (PCMs), (6) using combined heating and power (CHP), and (7) using natural ventilation.
At the end of the construction phase, commissioning is a crucial step to ensure the building is performing as the intended design and is meeting its objectives. Commissioning phase verifies that the building’s energy-related systems are installed and calibrated and perform according to the owner’s project requirements, basis of design, and construction documents. The commissioning phase should cover at least the HVAC systems and controls, lighting and daylighting controls, domestic hot water system and any renewable system such as wind and solar. Building commissioning can reduce energy use, lower operating costs, reduce contractor callbacks, and improve occupant productivity. Successful implementation of the commissioning process can yield 5–10% improvements in the energy efficiency.
Renewable energy measures
Go green! Maximizing the energy sources are done through the first two measures, the building envelope which promotes using less energy and the efficient utilities and equipment measures. The renewable energy measures are more expensive than these two measures, and for that designers should start with the first two measures and optimize their design which would reduce the energy requirement needed in this step.
There are various renewable energy resources, such as solar which can be used for generating electricity, storing energy, and heating water, wind, biomass systems, and other sources.
Solar water heating systems include roof-mounted solar collectors that heat a fluid which would be used to heat water stored in a cylinder. Two collector types are usually used: the flat plate and the evacuated tube type. Flat plate collectors are usually cheaper. The solar water collectors heat the water that would be stored in a cylinder directly or indirectly by heating another fluid that would heat the water. Photovoltaic systems can be used to store energy and help in shifting the peak load.
Wind systems provide energy a very effective cost if the wind is continuous and steady and its speed above 10 mph (4.47 m/s), but it is recommended to be above 25 mph (11.2 m/s).
Biomass systems could provide heat by burning the biomass material. Some examples include forests, urban tree pruning, farmed wastes, wood chips, or pellets. However, the burners usually require more frequent cleaning than oil and gas boilers.
Geothermal systems provide good source for both cooling and heating by running the refrigerant pipes under the ground that usually provide nearly constant temperatures. These systems do not produce emissions. Such systems can provide coefficient of performance of 3 or even higher.
In this section, different case studies will be presented that implemented sustainable development and net-zero energy principles. The cases were selected based on their impact as reduced energy consumption and optimized sustainable resources used for energy and water.
The Bullitt Center in Seattle was opened on Earth Day on April 22, 2013. The building is shown in Figures 4 and 5 and is rated as the greenest commercial building in the world. It is a six-story building and has a total area of 52,000 ft2 (4800 m2). The building is energy and carbon neutral, but its cost reaches as high as $18.5 million which yields $355 per square foot (per 0.09 m2). The center’s energy efficiency is 83% better than a typical office in Seattle with many efficient and sustainable energy sources including a 242 kW photovoltaic array, ground source geothermal heat exchange system, radiant floor heating and cooling, and retractable external blinds that block heat from warming the building. For water usage aspect, the center is 80% more efficient than a typical office in Seattle with live rainwater-to-portable water system that can collect up to 56,000 gallons (211,948 L) of rainwater [16]. The building also uses gray water reclamation using compositing foam flush toilets that save up to 96% of water as compared to traditional flush toilets. The building has also green roof and wetlands.
Seattle’s net-zero energy building (Bullitt Center) [17].
Seattle\'s net-zero energy building (Bullitt Center).
La Jolla Commons II is a 13-story office at the University Town Center which is considered to be one of the largest NZEB in the United States. The building has a total area of 415,000 ft2 (38,555 m2) and was completed in April 2014 in San Diego, California. The completed building is shown in Figure 6. The building is rated as pre-certified silver as per US Green Building Council and a potential building for LEED platinum. The building has slab on-grade foundation. Other sustainability features include low-emissive coatings that reflect invisible long-wave infrared (IR) heat, reduce heat gain or loss in the building, and provide greater light transmissions. The walls were all glass as shown in Figure 6 [18]. The air was supplied through underfloor air distribution (UFAD) system at 68 F (20°C). The cooling loads were 15 tons per floor and were supplied through two 560 tons cooling towers that served chillers located in the basement of the building. To achieve the net-zero energy efficiency, the building reduced the consumption through efficient designs and sustainable practices in addition to on-site generation. Fuel cells were generated at a rate of 5.4 megawatt-hour, whereas the historical expected consumption was approximately 4.5 megawatt-hour. The fuel cell technical data are shown in Table 1. The fuel cells are shown in Figures 7 and 8. The building is fed by biogas which would reduce energy costs. The cost per square footage was higher but it came with more benefits.
La Jolla Commons [18].
Inputs | |
---|---|
Fuels | Natural gas, directed biogas |
Input fuel pressure | 15 psi, gage (6.89 kPa, gage) |
Fuel required at the rated power | 1.32 MMBtu/h of natural gas |
Outputs | |
Base load output (net AC) | 200 kW |
Electrical efficiency (LHV net AC) | >50% |
Electrical connection | 480 V at 60 Hz, three- or four-wire three-phase |
Physical | |
Weight | 19.4 tons |
Size | 26\' 5" × 8\' 7" × 6\' 9" (8 m × 2.6 m × 2 m) |
Technical highlights for the La Jolla Commons fuel cells.
Fuel cells used at the La Jolla Commons building.
Fuel cells used at the La Jolla Commons building.
It is classified as one of the greenest buildings on the planet as depicted by the US Green Building Council Prez [19]. The project consists of three one-story buildings. The project is located in Baraboo, WI, with cold and humid air conditions, with over 11,900 ft2 area (1105 m2). It has a platinum rating from the USGBC LEED-NC with net-zero energy rating. The first features of this project were the reduction in water consumption which reached up to 65% through the usage of waterless urinals, dual-flush toilets, and efficient faucets. The other features were the efficient irrigation features implemented using crushed gravels instead of blacktop or concrete paving which increased the rainwater infiltration and helped in blending the developed areas with the surrounding landscape which eliminated the need for irrigation. The utmost feature for this project was the significant reduction in energy usage which reached to 70% less than a comparable conventional building by using 39.6 kW rooftop photovoltaic arrays that produces more than 110% of the project’s annual electricity needs. A sketch for the design is shown in Figure 9, and a picture showing the installed cells on the roof is shown in Figures 10 and 11.
Aldo Leopold Legacy Center in Wisconsin [20].
Photovoltaic cells used for the Aldo Leopold Legacy Center project [20].
Photovoltaic cells used for the Aldo Leopold Legacy Center project [21].
The buildings were oriented properly to have the maximum solar radiation source. Not only ground heat pumps were used as sources for heating and cooling, but Earth tubes were used to preheat and precool ventilation air, as well. Windows were utilized and properly oriented toward the south to get the maximum daylight that can reduce heat needs and lighting. The window area was maximized to optimize these two factors as shown in Figure 12.
Window orientation used to aid heating and lighting in the Aldo Leopold Legacy Center [21].
For additional heat, EPA-approved wood stove or fireplace was used. The final couple features were the usage of displacement ventilation and demand-controlled ventilation through the usage of variable frequency drives for fans that would control the amount of cooling or heating supplied to the spaces based on actual load and not the maximum designed.
The payback period for this project is expected to be around 14 years [20].
The center is located on the island of Hawaii and is used by the Natural Energy Laboratory of Hawaii. The center is used for energy and technology research and development. The center is shown in Figure 13.
Hawaii Gateway Energy Center [20].
Natural ventilation is used through copper roof that radiates heat from the sun into a ceiling plenum as shown in Figure 14. Fresh outdoor air is pulled through the natural ventilation process into the occupied space from a vented underfloor plenum. Seawater at around 45 F (7.2°C) is used to cool the air to 72 F (22.2°C) as shown in Figure 14. As with the Leopold Legacy Center, the building is properly oriented to benefit from daylighting that aids lighting and reduces the energy needed to light the interior of the building. In summer, to prevent the negative affect of solar heat gain, shades are used on all windows. The center uses photoelectric daylight sensors to control the lights in addition to occupancy sensors. This prompted lights to be off 100% during daylight hours.
Hawaii Gateway Center radiant roof system.
The building has 20-kW photovoltaic array which produces approximately 25,000 kW-hr due to high insolation in the area. Part of this power is used to power the pumps that draw seawater to cool the air and power the lights and other auxiliary electrical equipment. The building itself consumes 20% of the energy that comparable buildings use. In 2006, adjustments were made to the pumping systems which resulted in excess energy from the photoelectric system.
This chapter reviewed various techniques and designs that help achieve a net-zero energy building. The most important techniques are optimizing HVAC designs to reduce energy consumptions and usage of renewable sources. Some of the techniques include geothermal heat pumps, underfloor air distribution, radiant floor heating and cooling, retractable external blind on windows, and proper orientation of the building which would maximize heat gains in cold weather and minimize it in summer using trackable blinds, photoelectric daylight sensor, and occupancy sensor. Renewable sources include fuel and biomass cells, biogas, photovoltaic cells, and EPA wood stove for heating. Water usage as well could be optimized by using gray water reclamation and by using rainwater-to-potable live water systems.
Net-zero energy building design starts with ethical clients and demonstrators. Designers and users need to be lean in their designs to reduce the energy consumption, be clean by using energy-efficient utilities and systems, and be green by using renewable energy sources such as biomass, wind, solar, geothermal heat sink, and rivers. Canals could be a good source for heat pumps in cold weather regions [22].
Future buildings will focus more on renewable and sustainable energy resources by implementing an efficient building envelope and utilizing energy-efficient and high-performing utilities promoting reduced energy consumption levels. Future design will benefit from various potential energy resources including solar, wind, tidal, biomass, and other resources. Future system design and selection will need to simulate the various cases, variables, and scenarios to decide on optimized building design such as exposure, orientation, window to wall ratio, shading, building envelope, etc. In addition to that, artificial intelligence (AI) will play a major role in the operation and maintenance of such buildings including smart meters, smart display boards that recommend actions to tenants to reduce energy consumption, lighting control versus shading, and air-conditioning operation. Governments, local states, and cities have to commit to get this into track. They should facilitate sources access and should force using the guidelines and codes.
NZEB | net-zero energy buildings |
HVAC | heating, ventilation, and air-conditioning |
DOE | |
USGBC | US Green Building Council |
LEED | Leadership in Energy and Environmental Design |
LEED-NC | LEED-New Construction |
EPA | |
HEPA | high-efficiency particulate air |
CFM |
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