Anthropogenic Climate Change in an Integrated Energy Balance Model of Global and Urban Warming
 Kimitoshi Sato^{1}Email author
DOI: 10.1186/s4000801400099
© Sato; licensee Springer 2015
Received: 3 March 2014
Accepted: 18 November 2014
Published: 23 January 2015
Abstract
This paper presents an integrated energy balance model of global and urban warming in the attributes/functionings framework à la Gorman–Lancaster–Sen and proposes a Global Warming Function and an Urban Warming Function. Also presented is a concept of Heat Island Integral, which measures the difference of anthropogenic heat stocks between two regions. The model involves residents, producers such as offices and manufacturers, and landscape gardeners who play a very important role in cooling down by rooftop gardening and treeplanting activities, etc. It is shown that urban warming tax/subsidy scheme is designed as a Groves mechanism by the implementation theory.
Keywords
Anthropogenic heat stocks Attributes/characteristics à la Gorman–Lancaster Biological attributes Global warming function Heat island integral Landscape gardener Microclimate Sen’s functionings Urban warming function Urban warming tax/subsidy schemeJEL Classification
H2 Q24 R13 R141 Introduction
An urban heat island is represented by isoterms on a map joining points of equal temperature and it is an analogy of contours of above and beneath the sea. By using the concept of Heat Island Integral that I introduce below, formal definitions of a heat island and a cool island are given in Sect. 2.3.^{1}
In the past 100 years, the temperature has risen 0.9 °C in Japan and 3.2 °C in Tokyo.^{2} Whereas the temperature increase of Paris and New York are, respectively, about 0.9 °C and 1.6 °C for the same period. Tokyo’s urban warming rate was remarkable; it is above the rising rate of the past ten thousand years. The Tokyo Metropolitan Research Institute for Environmental Protection estimated that the heat emitted from cars and air conditioners has resulted in a temperature increase of 0.4 °C and from the loss of greenery it has increased by 1.4 °C in the past century. The green area of Japan was halved from 1930 to 1990, thus, there has been an increase in radiant heat and a decrease in radiation cooling. There is therefore a pressing need to manage the urban thermal pollution due to urban warming in many cities of Japan. See Sato (2013) for biohazards and health risks suffered from urban thermal pollution.
In this paper, let me present a model to provide an optimal amount of heat as an urban public good. In order for this model to be operational, necessity compels us to devise a tax/subsidy scheme to determine the sum of emissions of heat released by metropolises into the urban atmosphere. The urban environment should now be perceived to be an intergenerational public good that we have to protect. Large cities such as Tokyo, Osaka, Sendai, Hiroshima, Fukuoka, Nagoya, and Sapporo consume a huge amount of energy by using cars and air conditioners, hence, urban warming has now become notable. Metropolitan residents are to be involved in the problem of urban warming which is now confirmed to be caused by emissions of enormous heat, i.e., all the households living in cities could be polluters as well as victims of the warming climate. Any local government is in charge of controlling the total amount of heat emitted by residents and producers to keep the urban climate not too warm in the near future.
This paper proposes to consider urban atmosphere as a complex of intangible attributes such as heat and gases, and the goods composed of tangible attributes that are produced by firms, and green areas consisting of flowers and trees as biological attributes supplied by landscape gardeners.
The paper proceeds as follows. Section 2 presents an integrated energy balance model of global and urban warming in the attributes/functionings framework à la Gorman–Lancaster–Sen and proposes an Urban Warming Function. Also presented is the concept of Heat Island Integral, which measures the difference of anthropogenic heat stocks between two regions. The model involves residents, producers such as offices and manufacturers, and landscape gardeners, who play a very important role to cool down by rooftop gardening and treeplanting activities, etc. It is shown that an urban warming tax/subsidy scheme is designed as a Groves mechanism by the implementation theory. Finally some remarks follow, including some technological innovations.
2 Urban Warming and Heat Island
2.1 A Model of Urban Warming and Heat Island
This section introduces the attributes/characteristics model based on the Gorman–Lancasterian theory where goods are regarded as a composition of characteristics.^{3} All trace gases such as greenhouse gases (GHGs) can be interpreted as gaseous attributes in our framework, since they infinitesimally compose the urban atmosphere as an urban public good. Characteristics of urban climate are in order: pollution substances, solar radiation, cloudiness, precipitation, temperature, absolute and relative humidity, and wind velocity. These attributes compose the urban planetary boundary layer. This paper focuses upon heat as an attribute, since it is the main cause of urban warming. Before rushing into our theoretical model, let me introduce some basic concepts of urban warming and heat islands.
Let us consider a city where we analyze urban warming and heat islands and the related problems occurring in urban and suburban areas. For the sake of simplicity, assume that our city is composed of two areas, i.e., the urban area and the suburban area, which are divided into many regions, \(\beta \in \mathbf{B}=\{1,\ldots,B\}\): the set of regions. Assume that any size whatever can be chosen for a region.
Let there be N residents indexed by \(i\in \mathbf{N}=\{1,\ldots,N\}\): the set of inhabitants who live in both urban and suburban areas. Each individual emits heat and trace gases when consuming goods or services indexed by j and its set is \(\mathbf{J}=\{1,\ldots,J\}\). For the sake of simplicity, it is assumed that each producer j supplies only one good j which is composed of C characteristics indexed by \(c\in \mathbf{C}=\{1,\ldots,C\}\): the set of tangible attributes. Denote as \(q_{jc}\) an amount of attribute c embodied in one unit of good j. There are producers: e.g., offices, hotels, and manufacturers.
Suppose that resident i chooses a landscape gardener named ℓ to have a part of his/her land planted with trees and flowers, and \(\boldsymbol{\varLambda }=\{1,\ldots,\varLambda \}\) is the set of gardeners. Define \(q_{\ell s}\) as a biomass of species s in one cube meter supplied by landscape gardener ℓ, and \(\mathbf{S}=\{1,\ldots,S\}\) as the set of species of flora and fauna as biological attributes. Let \(x_{ij}\) be resident i’s consumption of good j, and \(V_{i\ell }\) be his/her demand for the plants supplied by landscape gardener ℓ, thus, \(x_{i}= ( x_{i1},\ldots,x_{iJ},V_{i\ell } ) \) is his/her consumption vector. There is also a local government whose task is to reduce heat emissions by making effective use of an urban warming tax scheme as defined below. No need to mention, every inhabitant, producer, and landscape gardener resides in some house or construction in region β, so that an index β will be omitted hereafter in almost all the cases, except for describing some variables related to region β.
 H1.
The city is formed in a heterogeneous plain, where the climate differs among its regions.
 H2.
The city is not necessarily circular and its center is called the Central Business District.
 H3.
Its urban and suburban transportation systems are available in any direction whatsoever.
 H4.
Residents commute to work for an office in the CBD or in suburbs.
 H5.
Landscape gardeners plant in a part of the lands of residents and producers.
 H6.
Manufacturers produce goods in the suburban area.
The urban atmosphere is regarded as a complex of gaseous attributes including GHGs, which are to be mainly generated by production and consumption activities. The amount of gases such as N_{2} and O_{2} are stationary, so I can focus upon heat and trace gases as attributes in this paper. Let \(\mathbf{G}=\{C+1,\ldots,C+G\}\) be the set of trace gases which compose the urban atmosphere.
In the above equations, \(z_{ic}\) means the consumption of tangible attributes which compose goods, while \(z_{g }\) and \(z_{h}\) represent the total amount of a trace gas and heat emitted by all residents, producers and gardeners. Note also that the values of \(z_{g}\), \(\forall g\in \mathbf{G}\), and \(z_{h}\) can be measured in tons or kilojoules. Heat and gases are generated both in the consumption and production of goods and services. Every inhabitant is made to consume not only his/her emissions but also the quantity emitted by the rest of the city. When he/she uses goods, he/she emits heat and gases. They are already released when the goods are made by producers and greening services are provided by landscape gardeners.
The above three equations may be interpreted as characteristics availability functions which convert commodities into attributes. In the framework of this paper, any good j can be recognized as \((x_{j},q_{j1},\ldots ,q_{jC+G})\) and any greening service ℓ can be represented as \((V_{\ell },q_{\ell C+1},\ldots ,q_{\ell C+G},q_{\ell C+G+1},\ldots ,q_{\ell C+G+S})\). The amount of any characteristic associated with each good and service can be regarded as a parameter that is objective and common to all consumers, i.e., it has the publicgood property. Thus, the inhabitants as consumers must behave as “price and quality takers,” since they can only change their consumption of \(z_{ic}\), \(z_{ih}\), and \(z_{ig}\), via the choice of \(x_{ij}\) and \(V_{i\ell }\), given the price and the quality of each good and service. Producers and gardeners can choose the composition of attributes embedded in their goods and their greening services.
 T::

temperature (°C)
 Al::

planetary albedo (0.3) determining how much of the incoming energy is reflected by the atmosphere
 Ω::

solar constant (1372 W m^{−2})
 ε::

emissivity (assumed to be 1)
 σ::

Stefan–Boltzmann constant (\(5.67 \times 10^{8}\mbox{ W}\,\mbox{m}^{2}\,\mbox{K}^{4}\)) [the outgoing flux is \(\varepsilon \sigma T^{4}\) by the Stefan–Boltzmann Law]
 K (kelvin)::

273.15 K = 0 °C
 \(\varUpsilon _{\beta }\)::

anthropogenic heat stocks at region β [J]
 \(\dot{T}_{\beta }^{t}\)::

temperature increase at region β at time t [°C]
 \(c_{p}\)::

specific heat capacity [1004.2 J/kg °C]
 \(u,v\)::

coordinates [m]
 M::

atmospheric density [1.293 kg m^{−3}]
 \(A_{\beta }\)::

airshed of region β [m^{3}]
 Ab::

a coefficient (0.3) determining how much of the energy which is not absorbed by the surface of the earth
2.2 Global Warming Function
It is observed that warming of cities is mainly due to heat emissions and partly due to global warming, and the GHGs’ concentrations affect the latter. These effects therefore must be incorporated in the model of urban and global warming.
As was mentioned in Sect. 2.1, \(z_{g}\), \(\forall g\in \mathbf{G}\), is the total quantity of each GHG released all over the world. A part, \(\alpha _{g}z_{g}\), \(0<\alpha _{g}<1\), \(\forall g\in \mathbf{G}\), of an aggregate emission of trace gas g, is observed to go to the atmosphere and the rest, \((1\alpha _{g})z_{g}\), is perceived to be absorbed by the oceans and forests as carbon sinks, if g is carbon dioxide. Of this amount, about 43 % of the CO_{2} emissions are observed to be absorbed. The mass of the gth GHG staying in the atmosphere is \(\alpha _{g}z_{g}\), \(\forall g\in \mathbf{G}\). The disintegration rate or an inverse of an atmospheric lifetime of each trace gas is denoted as \(\mu _{g}\), \(0<\mu _{g}<\alpha _{g}\), \(\forall g\in \mathbf{G} \).
In the sequel, let me follow Greiner (2004a, 2004b) for global warming in an endogenous growth model, originally due to Roedel (2001).
Compare the two values of temperature, i.e., 15 °C and 17 °C. The difference is 2 °C, which is attributable to the effect of GHGs’ concentrations between the years 1750 and 2004.
2.3 Heat Island Integral
The problem of how to represent anthropogenic heat stocks in any block was analyzed in Sato (2006) who introduced the concept of Heat Island Integral. Here a new version is proposed. In effect, there are differences in the temperature of building surface, back alleys, rooftops, streets, and green tracts of land, which are directly exposed to the solar radiation. These differences of the surface temperature of the ground coverage can be measured by utilizing infrared cameras or remote sensing.
A formula is proposed for heat as a stock in this subsection. It is the microclimate surrounding a construction, which most influences any agent who resides or works in any region. However, climatical incidents depend not only upon the heat stocks in each region, but also upon those in the entire city. More precisely, it is the sum of developable areas of the ground coverage, e.g., streets, tree crowns, rooftops, and walls of the buildings which exist in region β. Denote \(\kappa _{\beta }^{r}\) and \(\delta _{\beta }^{r}(u,v)\) as the area and the height of construction r in region β, respectively, and R as the set of constructions. Suppose β is an urban commercial region and \(\beta ^{\prime }\) is a suburban residential region.
Needless to say, the existence condition of this multiple integral is that the functions are continuous and compact in the domains \(\kappa _{\beta }^{r} \) and \(\kappa _{\beta ^{\prime }}^{r}\), and it is easily seen that this condition is satisfied. Region β is called a Heat Island if \(\mathit{HII}>0\). Naturally, it is necessary to consider meteorological conditions peculiar to region β, such as the Foehn phenomenon, the convergence of sea breezes, and the transport of the warmed air from other regions, as well as the configuration of the region such as being a basin. Region β is called a Cool Island if \(\mathit{HII}\leq 0\).
Remark 1
The difference between Heat Island Intensity and Heat Island Integral is obvious. The former shows the difference of the temperature between two regions, while the latter signifies that of the anthropogenic heat stocks between them. The temperature of asphalt and concrete is very often higher than that of the atmosphere in the summertime. It is observed that these materials absorb approximately 70 % of the solar radiation, so that the walls of buildings made of concrete absorb the same amount of heat, which results in urban warming. Thus, an area with a lot of these constructions is apt to become warmer. Notice that concrete is a material which is not at all “soon hot, soon cold,” but hard to be heated and hard to cool off.
2.4 Urban Warming Function
Let \(z_{ih\beta }\) be heat emitted by resident i and \(z_{jh\beta }\) (\(z_{\ell h\beta }\), resp.) is heat emissions of producer j (landscape gardener ℓ, resp.) at region β. Any city is composed of regions with anthropogenic heat stocks, \(\varUpsilon _{\beta }=\varUpsilon _{\beta }(E_{\beta })\), where \(E_{\beta }=\sum_{i\in \mathbf{N}}z_{ih\beta }+\sum_{j\in \mathbf{J}}z_{jh\beta }+\sum_{\ell \in \boldsymbol{\varLambda }}z_{\ell h\beta }\), \(\forall \beta \in \mathbf{B}\). With \(E=(E_{1},\ldots ,E_{B})\), the total heat stocks, \(\varUpsilon (E)=\sum_{\beta \in \mathbf{B}}\varUpsilon _{\beta }(E_{\beta })\), may affect agents in any city.
Assumption 1
For any \(\beta \in \mathbf{B}\), \(U_{\beta }^{t}\) is concave and twice continuously differentiable.
Remark 2
It can easily be seen that \(\partial U_{\beta }^{t}/\partial \varXi ^{t}>0\), \(\partial ^{2}U_{\beta }^{t}/(\partial \varXi ^{t})^{2}>0\), \(\partial \varXi /\partial \zeta _{g}>0\), \(\partial ^{2}\varXi ^{t}/(\partial \zeta _{g}^{t})^{2}>0\), \(\forall g\in \mathbf{G}\), \(\partial U_{\beta }^{t}/\partial \varUpsilon _{\beta }^{t}>0\), and \(\partial ^{2}U_{\beta }^{t}/(\partial \varUpsilon _{\beta }^{t})^{2}>0\), \(\forall \beta \in \mathbf{B}\).
Urban warming is a typical example of a public good which is nonrival but excludable. Its impact on each resident varies from region to region, which can be treated as a regional public good. The global warming function depends upon the anthropogenic heat stocks in region β, \(\varUpsilon _{\beta }\), and the concentrations Z composed of gaseous attributes of the urban atmosphere.
2.5 Beings and Functionings of Residents
The Gorman–Lancasterian characteristics theory is the most suitable to analyze goods and the urban atmosphere which is perfectly divisible and decomposable as various attributes. However, the characteristics availability functions can be applied to any resident whose utilization differs from person to person. Consequently, each inhabitant’s functionings should be introduced as one of the important concepts à la Sen (1985) to fully appraise the value of goods or their characteristics. Each resident’s physical and climatical situations differ, so I must introduce the functionings which are represented below.
Let \(\mathbf{K}_{i}=\{f_{i1},\ldots ,f_{ik},\ldots ,f_{iK_{i}}\}\), where \(K_{i}\) differs among individuals. The following assumption is needed.
Assumption 2
For any \(i\in \mathbf{N}\), \(f_{ik}\in \mathbf{K}_{i} \) is twice continuously differentiable.
2.6 Resident’s Happiness Function and Valuing WellBeings
Any person’s use of functionings can vary his/her being and happiness. Let \(\partial f_{ik}/\partial U_{\beta }\) and \(\partial U_{\beta }/\partial \varXi \) be \(f_{ikU_{\beta }}\) and \(U_{\beta \varXi }\), respectively. Let also \(\partial \varXi /\partial \zeta _{g}\) and \(\partial U_{\beta }/\partial \varUpsilon _{\beta }\) be \(\varXi _{g}\) and \(U_{\beta \varUpsilon }\), respectively. Denote \(\partial \zeta _{g}/\partial z_{ig}\) and \(\partial \varUpsilon _{\beta }/\partial z_{ih}\) as \(\zeta _{gz}\) and \(\varUpsilon _{\beta z}\), respectively.
Remark 3
 (i)
\(\pi _{ih}\) is a marginal contribution of heat as an attribute to resident i’s marginal happiness through his/her functionings in terms of his/her available time \(z_{i0}\). It may correspond to a marginal rate of substitution between each attribute and the time \(z_{i0}\) in the utility theoretical context.
 (ii)
Whether inhabitant i considers a commodity or a service as good, irrelevant, or bad to his or her functionings is confirmed by the sign of \(\sum_{c\in \mathbf{C}\cup \mathbf{G}\cup \{h\}}\pi _{ic}q_{jc}\) for each good j and \(\sum_{c\in \mathbf{S}\cup \mathbf{G}\cup \{h\}}\pi _{ic}q_{jc}\) for any service ℓ. Moreover, whether a commodity or a service is socially good or not may also be examined by summing over individuals of \(\sum_{c\in \mathbf{C}\cup \mathbf{G}\cup \{h\}}\pi _{ic}q_{jc}\) for any good j and \(\sum_{c\in \mathbf{S}\cup \mathbf{G}\cup \{h\}}\pi _{ic}q_{jc}\) for any service ℓ. Now, to keep the room open to the cool air, an air conditioner is one of the necessities for our comfortable urban life under urban warming, even if it does emit heat as a vexing byproduct. Consequently, \(\pi _{ih}<0\) holds for many people who feel displeased by the scorching heat due to urban warming. However, they wish to avoid heat, thus, \(\sum_{c\in \mathbf{C}\cup \mathbf{G}\cup \{h\}}\pi _{ic}q_{jc}\gg 0\) still prevails for j if it is an air conditioner. It cannot be helped, since everybody wants to keep his/her room cool, especially under a burning sun. It is not only heat but also the resulting high humidity, and actual and sensory high temperatures, that could lower some functionings of residents. This fact can be represented by \((dH_{i}/db_{i})(\partial b_{i}/\partial f_{ik})\sum_{\beta \in \mathbf{B}}f_{ikU_{\beta }}U_{\beta \varUpsilon }\varUpsilon _{\beta z}<0\), \(\forall f_{ik}\in \mathbf{K}_{i}\), \(\forall i\in \mathbf{N}\).
3 Optimizations Under Urban Warming and Heat Island
3.1 Residents
Consider that city dwellers know the risks of humaninduced future urban climate changes, and that they have an incentive to optimize the composition of the urban atmosphere in order to aim at achieving their personal bestbeings in the city where they live and work.
Let e be a generic index for any emitter and E the set of all emitters in any city. Since heat and gases are generated by the use of fossil fuels, let \(\varepsilon _{e}\) be emitter e’s integrated emissions of heat and gases and denote \(\varepsilon _{e}=(\varepsilon _{1},\ldots ,\varepsilon _{e1},\varepsilon _{e+1},\ldots , \varepsilon _{N+J+\varLambda })\). Urban warming is a “privately provided regional public good” that is supplied by individual emitters of heat in the atmosphere. By emitting heat, which means using the urban atmosphere, every metropolitan infinitesimally contributes to hot air as an urban public good. The inhabitants and producers in an urban heat island are both members who are forced to join in an “urban club.”
Denote \(\nu _{i}(U(\varepsilon _{i}(\alpha _{i}),\varepsilon _{i}))\) as individual i’s damage function. A variable \(\alpha _{i}\geq 0\) is the abatement cost associated with his/her effort to avoid damages due to too much warmed urban air by reducing heat and gas emissions. It is assumed that \(\alpha _{i}\) is known only to individual i. Functionings to cool cities are, for example, economizing in power by reducing the use of electrical fittings and by using a bicycle or a public transportation system instead of a private car. As urban warming accelerates, city dwellers will want to buy newly developed, more efficient air conditioners, which result in reduction of heat emissions. These are examples of functionings which explain \(\alpha _{i}\). Resident i has to pay \(t_{i}(\varepsilon _{i}(\alpha _{i}))\) as an urban warming tax, in order for the urban atmosphere not to be warmed so much as to be unendurable to live in region β. It is natural to consider \(t_{i}(\varepsilon _{i}(\alpha _{i}))< t_{i}(\varepsilon _{i}(0))\), since paying an abatement cost could reduce emissions and his/her tax, which can incite people to behave environmentfriendly.
Greening lands and rooftops belong to the most effective ways to cool microclimates. The metropolitan government determine \(0<\varphi <1\) as the refund rate for planting the vegetation \(V_{i\ell }\) that resident i requests landscape gardener ℓ. Assume that the value of φ is decided by the scientific data about treeplanting. As defined, \(\sigma _{i\ell }\) is landscape gardener ℓ’s greening cost per cubic meter of inhabitant i’s garden, hence, \(\sigma _{i\ell }V_{i\ell }\) is resident i’s greening cost, and \(\varphi \sigma _{i\ell }V_{i\ell }\) is i’s refund for the effort to plant trees in his/her garden.
Assumption 3
For any \(i\in \mathbf{N}\), \(t_{i}\), \(\nu _{i}\), and \(\varepsilon _{i}\) are convex, and they are continuously differentiable, with \(\partial \nu _{i}/\partial U_{\beta }>0\), \(\partial U_{\beta }/\partial \varepsilon _{i}>0\), \(d\varepsilon _{i}/d\alpha _{i}<0\), and \(dt_{i}/d\varepsilon _{i}>0\), \(\forall \beta \in \mathbf{B}\).
Remark 4
 (i)The conditions presented are not only necessary but also sufficient from the assumptions on the functions. In the first equation, \(\pi _{ic}\) signifies a hedonic shadow price of attribute c acquired by utilizing inhabitant i’s available time and his/her functionings. The lefthand side of the first equation is the sum of resident i’s marginal evaluations of the tangible attributes embodied in one unit of a good, as well as of the gaseous attributes and heat released when the good is produced. Notice that the first two formulas verify that any resident considers heat and gases as intangible characteristics emitted when consuming one unit of good j. The first conditions mean that the unit price of the good is equal to the sum of marginal contributions of attributes to his/her happiness through his/her functionings. The conditions assure a Pareto optimality for a quantity of each good, and they give a basis upon which goods resident i chooses to buy. He or she may not buy good j after due consideration of \(\sum_{c\in \mathbf{G}\cup \{h\}}\pi _{ic}q_{jc}\), which may be smaller than \(p_{j}\), because \(\pi _{ic}q_{jc}<0\) holds for some \(c\in \mathbf{C}\) and$$ \sum_{c\in \mathbf{C}\cup \mathbf{G}\cup \{h\}}\pi _{ic}q_{jc}<\sum _{c\in \mathbf{C}}\pi _{ic}q_{jc}=p_{j}. $$(36)
 (ii)
The second condition signifies that individual i’s marginal evaluation of species as biological attributes by having the vegetation \(V_{i\ell }\) in the area \(A_{i\ell }\) of his/her land \(L_{i}\), planted by landscape gardener ℓ is equal to his/her greening cost per cubic meter minus the refunded cost. The term \(\sigma _{\ell }\varphi \) may be called a “urban warming (alleviating) subsidy,” since it represents the reward according to the person’s effort to plant trees in a part of his/her land. Many residents suffer from the fierce heat in summertime, if he/she feels very displeased by the boiling weather due to urban warming.
 (iii)
The condition about \(t_{i}\) shows that city dweller i’s marginal evaluation of consuming a unit of electricity is a match for his/her marginal urban warming tax. Thus, a proper incentive is given to an inhabitant to have a part of his/her land planted with trees and flowers from motives of selfishness.
3.2 Offices and Manufacturers as Producers
Here I present the optimization by profit maximizing producers to supply one good with an optimal product quality to consumers. Let producer j (landscape gardener ℓ) produce good j (service ℓ) by using \(x_{j0}\) (\(x_{\ell 0}\)) as inputs, and the price of \(x_{j0}\) (\(x_{\ell 0}\)) is normalized to be one, with \(\sum_{j\in \mathbf{J}}x_{j0}+\sum_{\ell \in \boldsymbol{\varLambda }}x_{\ell 0}\leq \sum_{i\in \mathbf{N}}z_{i0}\). Then \(x_{j0}\) (\(x_{\ell 0} \)) is the amount of labor time that producer j (landscape gardener ℓ) uses as an input.
Denote \(\nu _{j}(U(\varepsilon _{j}(\alpha _{j}),\varepsilon _{j}))\) as producer j’s damage function and \(\alpha _{j}\geq 0\) is an abatement cost only known to j. Note that \(\nu _{j}\) depends on the emissions of the rest of the city. It may be interpreted as an external cost to buy, for example, more efficient power saving air conditioners. Urban warming tax \(t_{j}\) is a function of \(\varepsilon _{j}\) and \(\alpha _{j}\) represents producer j’s effort to decrease emissions of heat and gases when producing and transporting \(x_{j}=\sum_{i\in \mathbf{N}}x_{ij}\) units of good j. More examples to explain \(\alpha _{j}\) are in order: producer j encourages his/her staff to commute by bicycle, to use hybrid or fuel cell cars or electric vehicles as delivery vans, and to choose energysaving types of personal computers in its office.
It is generally accepted that midtown hotels and office buildings use more computers and air conditioners than residents and landscape gardeners. The former would emit more heat and gases into the urban atmosphere as to cool hotels and offices, as urban warming accelerates in the near future. As producers, offices offer services, manufacturers supply products. \(\sigma _{j\ell }V_{j\ell }\) is producer j’s greening cost, and \(\varphi \sigma _{j\ell }V_{j\ell }\) is the refund to j.
Assumption 4
For any \(j\in \mathbf{N}\), \(\psi _{j}\) is convex and twice continuously differentiable with \(\partial x_{j0}/\partial q_{jc}>0\), \(\forall c\in \mathbf{C}\cup \mathbf{G}\cup \{h\}\), \(c\neq j^{\prime }\). Furthermore, \(x_{j}>0\) implies \(x_{j0}>0\), and \(\forall \eta \in \mathbf{R}_{+}\), \(\{y_{j}\psi _{j} ( y_{j} ) \leq 0, x_{j0}\leq \eta \}\) is compact.
It is assumed that \(\pi_{ic}\) and \(\pi_{ig}\) are truthful, since all goods are private goods or publicly provided goods such as gas, water, and electricity, for which the residents have to pay public utility charges. Hence, they cannot have them for free.
Here I make another assumption.
Assumption 5
For any \(j\in \mathbf{J}\), \(t_{j}\), \(e_{j}\) and \(t_{j}\) are convex, and they are twice continuously differentiable with \(dt_{j}/d\varepsilon _{j}>0\), \(d\varepsilon _{j}/d\alpha _{j}<0\), \(\partial \nu _{j}/\partial U_{\beta }>0\), \(\partial U_{\beta }/\partial \varepsilon _{j}>0\), \(\forall \beta \in \mathbf{B}\).
Remark 5
 (i)
The first equation establishes a Pareto optimality for an amount of each attribute and determines a vector of optimal tangible characteristics embodied in the good supplied by producer j. The L.H.S. of the first equation is the marginal revenue which is the aggregate of the residents’ marginal evaluations of a change in an attribute embedded in \(x_{j}\). Its R.H.S. is the marginal cost in terms of labor time to produce \(q_{jc}\). \(\sum_{i}\pi _{ic}x_{ij}\) is the marginal social value of good j, which is the sum of the personal evaluations of a change in an attribute when the quantity of good \(x_{j}\) is produced.
 (ii)
The third equation shows a Pareto optimal quantity of each gas as an intangible attribute. The L.H.S. is the social value of heat, and the R.H.S. consists of the terms: the first two term is the marginal cost in terms of \(x_{j0}\), and the second term means the marginal climatic damage to emit heat. \(t_{j}\) is the urban warming tax of producer j.
3.3 Landscape Gardeners
Next, efficiency conditions for landscape gardeners are derived. Their job is to plant trees in areas of lands that residents and producers possess, so they are exempted from the obligation of greening a part of their own lands in our model. They supply plants as biological, and thus, tangible attributes, as well as intangible attributes.
Denote \(\nu _{\ell }(U(\varepsilon _{\ell }(\alpha _{\ell }),\varepsilon _{\ell }))\) as landscape gardener ℓ’s heat abatement cost and \(\alpha _{\ell }>0\) is a parameter only known to gardener ℓ. Landscape gardeners can attempt to serve green areas to residents and producers by using a new technology which does not emit too much heat. Let \(\mathbf{N}_{\ell }\) be the set of residents who commission landscape gardener ℓ to plant trees and \(\mathbf{J}_{\ell }\) be the set of producers which ask gardener ℓ to plant trees \(V_{\ell }=\sum_{i\in \mathbf{N}_{\ell }}V_{i\ell }+\sum_{j\in \mathbf{J}_{\ell }}V_{j\ell }\).
Two assumptions are needed for this maximization problem.
Assumption 6
For any \(\ell \in \boldsymbol{\varLambda }\), \(\psi _{\ell }\) is convex and twice continuously differentiable with \(\partial x_{\ell 0}/\partial q_{\ell c}>0\), \(\forall c\in \mathbf{S}\cup \mathbf{G}\cup \{h\}\), \(c \neq \ell ^{\prime }\). Furthermore, \(A_{\ell }>0\) implies \(x_{\ell 0}>0\) and \(L_{\ell }>0\), and \(\forall \eta \in \mathbf{R}_{+}\), \(\{y_{\ell }\psi _{\ell }(y_{\ell })\leq 0, x_{\ell 0}\leq \eta , L_{\ell }\leq \eta \}\) is compact.
Assumption 7
For any \(\ell \in \boldsymbol{\varLambda }\), \(t_{\ell }\), \(\varepsilon _{\ell }\) and \(\nu _{\ell }\) are convex and twice continuously differentiable with \(dt_{\ell }/d\alpha _{\ell }<0\), \(d\varepsilon _{\ell }/d\alpha _{\ell }<0\), \(\partial \nu _{\ell }/\partial U_{\beta }<0\) and \(\partial U_{\beta }/\partial \varepsilon _{\ell }<0\), \(\forall \beta \in \mathbf{B}\).
Remark 6
The equations establish a Pareto optimality for the amount of each attribute and determine a vector of optimal quality characteristics that any gardener can supply its biological product to residents and producers. In the second and third equations, the R.H.S. are composed of two terms: the first is the marginal cost of the labor to supply one unit of plant as a biological attribute and the second term is gardener ℓ’s marginal contribution to urban warming by emitting heat. The L.H.S. of the equations signify the marginal social value in terms of the labor time, where the marginal social value is the sum of the evaluations of a change in each biological characteristic.
3.4 Urban Warming Tax and Subsidy
An assumption is imposed.
Assumption 8
\(D_{\beta }\) is concave and twice continuously differentiable with \(\partial D_{\beta }/ \partial U_{\beta }>0\) and \(\partial ^{2}D_{\beta }/\partial U_{\beta }^{2}>0\), \(\forall \beta \in \mathbf{B}\).
Here is the main result.
Theorem 1
Proof
In the above equation, S interpreted as the amount of subsidy can be refunded to those collaborating on treeplanting plus the costs of public utilities. Let me propose therefore the following.
Claim 1
Subsidies are, respectively, given to residents, offices, and manufacturers, since they have cooperated in their efforts to have trees and flowers planted in the required percentage of their land lots. An important feature is that the tax levied may fully cover social damages, and the part of the tax paid S can be redistributed to the contributors in order to cool their city.
4 Final Remarks
This paper has analyzed urban warming and heat island in the theory of attributes/functionings à la Gorman–Lancaster–Sen that I proposed in Sato (2008). My discussion has proceeded on the premise that the urban atmosphere is a composite of intangible characteristics including heat. This paper has extended Sato (2006, 2008) to combine global and urban warming and the urban heat island in an integrated energy balance model. Our model incorporates landscape gardeners who are commissioned by residents and producers. Then an optimization by each agent is solved to derive optimality conditions in the attributes/functionings theory. Residents are happiness maximizers and producers and landscape gardeners are profit maximizers, and the metropolitan government is a social cost minimizer. An urban warming tax/subsidy scheme has been proposed; the subsidy is given to contributors of cooling the city, by planting. This paper has also shown that the change of composition of tangible attributes in the goods changes that of intangible attributes such as heat and GHGs in the urban atmosphere.
As a recent technological innovation, let me introduce the photocatalyst of titanic oxide (TiO_{2}) to cooldown structures. This method clarified that water can be decomposed only by photo energy and titanic oxide. In 2006, an experiment was conducted on a rooftop (10 m^{2}) of a building, which was covered by a water film coated with titanic oxide. This test proved that this film of water could cool the building and showed that the temperature decreased by 30 °C. More precisely, that experiment verified that the mercury stood at 60 °C without the photocatalyst and water sprinkling, whereas the temperature was 30 °C with both. The maximum temperature difference between the two cases amounted to 30 degrees. The indoor temperature at that time was 15 °C, which resulted in the cost reduction of air conditioning. The photocatalyst of titanic oxide on glass on the sides of the buildings can cool down their structures and save on the cost of air conditioning. The cooling effect and cost effectiveness could be augmented by utilizing rainwater and by coating windows with titanic oxide. Currently, the size of the market for this technology amounts to 0.4 billion dollars, and it is anticipated to augment to 8.3 billion dollars in the future. In 2006 also, a new variety of photocatalyst has been discovered; applying the radiant energy resolves water to raise hydrogen, which is well known as an ultimate clean energy. A cocatalyst added to yellow powder as a composite of nitrogen gallium and zinc oxide becomes a catalyst which reacts by radiant energy. The resolution efficiency of water is about ten times higher than the former one and there is still room for enhancing further efficiency. In 2009, a new system of photocatalysis, the titania photocatalyst sheet was invented.
In 2008, it was proposed that a Sierpinsi manifold could be an alternative to the leaves of trees to cool down warming cities by discovering the fractal similarity of the former and the latter. Seen from one direction, a Sierpinski manifold is a plane, whereas it is threedimensional when it is seen from the other. By selecting a tree, it has been observed that its fractal is twodimensional, although it has a threedimensional structure. Samples of the Sierpinski manifold were made and placed on the roof of a building in a central business district in a city and obtained the desired result of cooling down by mitigating solar heat and light under their structure. It was verified that the trees have two fractal dimensions which are the same as the Sierpinski Tetrahedron. A roof as a complex of many Sierpinski tetrahedrons could be a substitute to trees, in terms of an efficient method to combat against urban warming and heat island. Some experiments were conducted by constructing roofs made by Sierpinski tetrahedrons and showed that the temperature beneath these roofs was lower than that measured on a road without the roofs. What is important is that maintenance and waterworks are not necessary for these manifolds, which could save on the cost of water. Different from trees, water is not necessary and just the management of roofs is needed.^{7}
As in Green et al. (2007), we must challenge ourselves to work towards stabilizing the urban climate by reducing anthropogenic heat stocks in regions of cities at all costs. We cannot foresee what will happen in the near future, so we had better take every precaution against urban warming and heat islands.
Urban heat islands exist in Tokyo’s central business districts (CBD) such as Otemachi, Shinjuku, and Shibuya. The Imperial Palace, the Meiji Shrine, and the Shinjuku Gyoen National Garden are Cool Islands, and the temperature of these areas remains rather low compared to the hotter spots mentioned above. Japan has warmed by 0.6 °C in these three decades. See Howard (1833, 1837) for the case of England and Renou (1862, 1868) for the case of France.
For the New Consumer Theory, see Gorman (1956/1980), Gorman and Myles (1987), and Lancaster (1966, 1971, 1991). See also Hagen (1975), Drèze and Hagen (1978), and Pendleton and Shonkwiler (2001).
Declarations
Acknowledgements
An earlier version of this paper was presented at the annual meeting of the Society for Environmental Economics and Policy Studies held at the Graduate School of Environmental Sciences, Tohoku University, September 16, 2012. Its revised version was presented at the autumn meeting of the Japanese Economic Association held at Kanagawa University, September 16, 2013. The author gratefully acknowledges Professor Toyoaki Washida for his useful comments and suggestions at that meeting. Some revisions were made thereafter.
Open Access
This article is distributed under the terms of the Creative Commons Attribution Noncommercial License which permits any noncommercial use, distribution, and reproduction in any medium, provided the original author(s) and source are credited.
Authors’ Affiliations
References
 Drèze J, Hagen K (1978) Choice of product quality: equilibrium and efficiency. Econometrica 46:493–513 View ArticleGoogle Scholar
 Gartland L (2008) Heat islands: understanding and mitigating heat in urban areas. Earthscan, London Google Scholar
 Gorman W (1956/1980) A possible procedure for analyzing quality differentials in the egg market. Journal paper 3129, Iowa Agricultural Experiment Station; Rev Econ Stud 47:843–856 Google Scholar
 Gorman W, Myles D (1987) Characteristics. In: Eatwell J, Milgate M, Newman P (eds) The new Palgrave dictionary of economics. Macmillan, London, pp 403–406 Google Scholar
 Graedel T, Crutzen P (1995) Atmosphere, climate, and change. W. H. Freeman and Company, New York Google Scholar
 Green C, Baksi S, Dilmaghani M (2007) Challenges to a climate stability energy future. Energy Policy 35:616–626 View ArticleGoogle Scholar
 Green J, Laffont JJ (1979) Incentives in public decisionmaking. Studies in public economics, vol 1. NorthHolland, Amsterdam Google Scholar
 Greiner A (2004a) Anthropogenic climate change in a descriptive growth model. Environ Dev Econ 9:645–662 View ArticleGoogle Scholar
 Greiner A (2004b) Global warming in a basic endogenous growth model. Environ Econ Policy Stud 6:49–73 View ArticleGoogle Scholar
 Groves T (1976) Information, incentives, and the internalization of production externalities. In: Lin S (ed) Theory and measurement of economic externalities. Academic Press, New York, pp 63–83 Google Scholar
 Hagen K (1975) On the optimality of the competitive market system in an economy with product differentiation. Swed J Econ 77:443–458 View ArticleGoogle Scholar
 Hof J, Rideout D, Binkley D (1990) Carbon fixation in trees as a micro optimization process: an example of combining ecology and economics. Ecol Econ 2:243–256 View ArticleGoogle Scholar
 Howard L (1833) Climate of London deduced from meteorological observations, 3rd edn. Harvey and Darton, London Google Scholar
 Howard L (1837) Seven lectures on meteorology. J Lucas Printer, MarketPlace, Pontefract Google Scholar
 IPCC (1990) Climate change: the IPCC scientific assessment. Cambridge University Press, Cambridge Google Scholar
 Laffont JJ (1982) Cours de théorie microéconomique, volume 1 – fondements de l’economie publique. Editions Economica, Paris. The revised and translated version: Bonin J, Bonin H (1988) Fundamentals of public economics. MIT Press, Cambridge Google Scholar
 Lancaster K (1966) A new approach to consumer theory. J Polit Econ 74:132–157. Reprinted as Chap 2 in Lancaster (1991) View ArticleGoogle Scholar
 Lancaster K (1971) Consumer theory: a new approach. Columbia University Press, New York Google Scholar
 Lancaster K (1991) Modern consumer theory. Edward Elgar, Hants Google Scholar
 Michaelis P (1990) Global warming: efficient policies in the case of multiple pollutants. Environ Resour Econ 2:61–78 View ArticleGoogle Scholar
 Myles G (1995) Public economics. Cambridge University Press, Cambridge View ArticleGoogle Scholar
 Pendleton L, Shonkwiler J (2001) Valuing bundled attributes: a latent characteristics approach. Land Econ 77:118–129 View ArticleGoogle Scholar
 Renou E (1862) Différences de temperature entre Paris et ChoisyleRoi. Annu Soc Fr 10:105–109 Google Scholar
 Renou E (1868) Différences de temperature entre la Ville et la Compagne. Annu Soc Fr 14:83–97 Google Scholar
 Roedel W (2001) Physik unsere Umwelt – Die Atmosphäre. Springer, Berlin Google Scholar
 Sato K (2006) Urban heat island: an environmental economic modeling. J Heat Isl Inst 1:40–45 Google Scholar
 Sato K (2007) Incentives in the hedonic MDP procedures for the global warming as a composition of gaseous attributes. Presented at the workshop of the environment of CORE at l’Université Catholique de Louvain, April 19; also presented at the regional science workshop in Sendai held at the Graduate School of Information Sciences, Tohoku University, July 26. Google Scholar
 Sato K (2008) Cooling the Metropolis: an economic analysis to alleviate urban heat island. J Heat Isl Inst 3:1–15 Google Scholar
 Sato K (2013) Biohazards and health risks due to urban warming. Presented at the annual meeting of the Society for Environmental Economics and Policy Studies, held at Kobe University, September 23. Google Scholar
 Sato K (2014) Ambivalence of water: beneficial and detrimental features. In: Langager M, Hashimoto J (eds) Water literacy: what will the next generation need to know? Monograph series, vol 7. International Christian University IERS, Tokyo, pp 25–33 Google Scholar
 Schneider S (1989) Global warming: are we entering a greenhouse century? Sierra Club Books, San Francisco Google Scholar
 Sen A (1985) Commodities and capabilities. Elsevier, Amsterdam Google Scholar
 von Thünen J (1826) Der isolierte Staat in Beziehung auf Landwirtschaft und Nationalökonomie: Untersuchungen über den Einfluß, den die Getreidepreise der Reichtum, des Bodens und die Abgaben auf den Ackerbau ausüben. Friedrich Perthes, Hamburg. English translation: Wartenberg C (1966) Von Thünen’s isolated state. Pergamon Press, Oxford Google Scholar