Green growth: an environmental technology approach.
Samad, Ghulam ; Manzoor, Rabia
This research is focused on achieving green growth through an
environmental technology approach. Developing environmental technology
we examined four elements considering the enforcement of intellectual
property rights (IPRs), research and development (R&D) expenditures,
the size of the market capture by GDP and most importantly the
environmental taxations. This study includes the 11 developed countries
which are Austria, Australia, Canada, France, Japan, Finland, Germany,
Sweden, U.K and U.S. Technology change can be better handled by panel
data than by pure cross-section or pure time series. It can minimise the
bias if we used the aggregate individuals or firms. Estimation
techniques depend on short panel or long panel. This study used the
Pooled Least Square estimation techniques like Fixed Effect Model (FEM)
and random effect model (REM) for both balance period of 2000-2005 and
unbalanced period from 1995-2005. The study concluded the policy
formulation in making developed's climate resilient economies.
JEL classification: O34, F19, L24
Keywords: Intellectual Property Rights, Foreign Direct Investment,
Technology Licensing
1. INTRODUCTION
Green growth policies provide strategies to overcome the economic
policies, which have devastating impact on the sustainability of the
country growth pattern. The growth that sustains development and
increases the opportunities of jobs and income with low environmental
degradations. Sustainable economic growth is achieved through the green
environmental technologies to maintain and restore environmental quality
and ecological integrity, while meeting the needs of all people with the
lowest possible environmental impacts. It is a strategy that seeks to
maximise economic output (GDP) while minimising the ecological burden.
(1) United Nations Economic Social Commission for Asia and Pacific
(UNESCAP) in his theme paper on green growth based green growth on five
tracks namely, (a) green tax and budget reform, (b) development of
sustainable infrastructure, (c) promotion of sustainable consumption and
production, (d) greening the market and green business, (e)
economic-efficiency indicators. One of the basic purpose of the green
growth is to facilitate green accounting, economist are of the view that
there is need for GDP measuring to include green accounting as the
existing national income accounts excludes environment. The growth,
which considered the inter-temporal welfare considered the social
discount rate, aggregate supply and demand analysis in the context of
environmental degradation and considering the structure change of the
economy is defined as green growth.
In recognition of the global challenges the rapidly rising green
house gases emission is one of the important challenges the
ecology/ecosystem has to face. The International Energy Agency (IEA)
technology perspective assess the strategies to reduce the carbon
dioxide (C[O.sup.2]) emissions to 14 Gt for 2050 keeping the 2005 as a
baseline emission 62 Gt. The cost effective combination of technologies
to reduce the C[O.sup.2] emissions from the baseline of 62Gt to 14Gt
are: Carbon dioxide Capture and Storage (CCS) industry and
transformation (9 percent), CCS power generation (10 percent), nuclear
(6 percent), renewables (21 percent), power generation efficiency and
fuel switching (7 percent), end use fuel switching (11 percent), end use
electricity efficiency (12 percent), and end use fuel efficiency (24
percent).
The reduction in GHGs requires technological change; technologies
at general and cleaner technologies specifically are useful for
development of most the low carbon economies. Technology includes all
tools, machines, instruments, housing, clothing, communication and
skills etc, which we used to produce new things and are very meaningful
in growth and development. Green technology is defined as: "The
development and application of products equipment's and system used
to conserve natural resources and environment which minimise and reduces
the negative impacts of human activities." (2) There are four
pillars of green technology policy namely energy, environment, economy
and social. In energy technology promote the efficient uses of
resources. Technologies conserve and protect the environment and
minimise the adverse impacts in environment, improve the economic
development through the technology and innovation. Moreover, the
International Technology Center (ITC) defined the green technology as:
"Goods and services to measure, prevent and limit pollution, to
improve environmental conditions of the air, water, soil, waste and
noise related problems which are affordable, adaptable and available at
the market of distributed use and export" This study is considering
technological opportunities as the development of green technology,
transfer of green technology and diffusion of green technologies.
1.2. Accelerating the Climate Change Technology
Eco-innovation strategies are needed to accelerate climate
technologies vis a vis to overcome the market barriers that exist all
along the technology development chain for mitigation and adaptation
technology. The markets for climate technology are imperfect and
extensive with barriers to full and fast market diffusion. Therefore
more innovative, internationally coordinated and integrated innovation
strategies are needed to scale climate technology at the speed needed to
counter climate change impacts. Public private strategies are needed to
complement pricing mechanism and enabling polices.
Limiting the concentration of green house gases in the atmosphere
is largely a problem of technological innovation. Climate innovation
polices will be necessary to accelerate rates and performance
improvements and cost reduction of technologies. (3)
1.3. Access to Climate Technologies
Climate change presents significant challenges for developing
countries. Therefore developing countries urgently need the climate
change technologies. Developing countries need to employ climate change
technologies in order to prevent climate disaster. Climate change
technology development will benefit developing countries directly by
providing useful technologies due to the support for endogenous climate
change, research and development, management of developing countries
intellectual assets, climate change technology, commercialisation,
awareness programs and periodic assessment. International climate change
discussion leading to Copenhagen and beyond present and provide
opportunities to link climate change technology transfer with
development of national innovation systems in order to achieve concrete
results for developing countries. Intellectual property rights will have
to become a tool of developing countries in their struggle to gain
access to climate change technology.
To assess these technologies faces some barriers like economic,
human capacity related barriers and institutional barriers. Smaller
developing countries are confronted with many such barriers to
development and transfer of technology. A range of economic and trade
related instruments provide opportunities for multilateral action to
promote climate-relevant innovation and technological transformation
provide, an "enabling environment". Governments of the
developed and developing countries start a number of programs focusing
on green innovation and emphasise the renewable energy resources in
2008-2009. Development and transfer of technology has emerged as a basic
building block in the crafting of a post 2012 global regime on climate
change. New government involvements in R&D programs may prove to be
beneficial in this regard and climate negotiators representing
governments should be better able to influence the direction of
industry. The private sector may be encouraged to extend the benefits of
new technology by entering into mutually beneficial arrangements with
foreign joint venture partners.
1.4. Environmental Innovations
Eco-innovation strategies are needs to accelerate climate
technologies visa vis to overcome the market barriers that exist all
along the technology development chain for mitigation and adaptation
technology. Therefore more innovative, internationally coordinated and
integrated innovation strategies are needed to scale climate technology
at the speed needed to counter climate change impacts. Climate
innovation polices will be necessary to accelerate rates and performance
improvements and cost reduction of technologies. The green environmental
technologies focus on innovations. In the global debate the
environmental innovations are taking place as of inventions and
innovations in general. Innovation in environmental technologies can
reduce the cost of materials, cost of productions and increase the rates
of production and attractiveness of products in marketplace.
To support the development of environmental technology the four
areas like intellectual property rights, research and development,
market size (GDP) and environmental taxation are very important.
1.4.1. Environmental Innovation and Intellectual Property Rights
(IPRs)
Recent years have witnessed a growing trend towards the
appropriation of climate change technologies by intellectual property
rights (IPRs). If this trend is to continue, IPRs are likely to play a
key role in determining access to these technologies. If highly priced,
access to protected interaction between Intellectual Property and the
transfer of climate related technology could provide the basis for more
efficient and evidence-based discussion. In developing countries the
strengthening of Intellectual Property Rights regime speed up the global
competition for capital and green technology [Maskus (2005)].
International Center for Trade and Sustainable Development [ICTSD
(2008)] presented that the IPRs promote innovation and knowledge.
Relationship of IPRs and transfer of climate related technology would be
helpful to increase the awareness and understanding. IPRs have deep
implications for the future of global warming, reduction of emission and
energy saving technology. A clean technology industry depends on
stronger protection of IPRs eventually the stronger IPRs regime speed up
the process of innovation and development. Relationship between the IPRs
and entrance in environmentally sound technologies leave the impact on
technological progress, development, and economic growth [Maskus
(2010)].
The above discussion concludes that through proper enforcement of
intellectual property rights can achieve the development in
environmental technology. Intellectual property plays a crucial role in
trade and technology transfer. The enforcement of IPRs encourages
economic growth and provides incentives for technology innovation.
Similarly, the enforcement of IPRs encourages transfer of climate
related technologies. The World Bank's Global Economic Prospects
Report in (2002) confirms, "Across the range of income level, IPRs
are associated with greater trade and FDIs flows, which in tuna
translate into foster rate of economic growth and development".
Eventually, this flow of FDIs leads to the development of environmental
technologies. The required and acceptable IPRs regimes bring efficiency,
new innovations and the progress in research and development, which
contribute into the development of environment technologies in the
economy.
1.4.2. Environmental Innovation and Research and Development
(R&D)
Research and development (R&D) expenditures is an essential
part of climate policy, might lead to substantial efficiency gains and
help containing climate policy costs. R&D induced by a climate
policy might a need for additional R&D expenditure policy in ordered
to foster technology diffusion and to overcome the various innovation
market failures such as the underinvestment in R&D in the private
sector. Active research and development created the new production of
knowledge and technological change. New research and development
produced the high quality of goods. Research and development increased
because the higher degrees of technology transfer [Walz (1995)].
Research and development increases the innovation in environmental
technology [William, et al. (1995)]. Developing countries successfully
reduced the GHGs emissions through the research and development
expenditures and achieved the energy efficient technologies [David and
Roger Bate (2010)]. In contrary Langinier, et al. (2009) extended the
arguments that the innovations factor leads to the research and
development.
The above discussion briefly concludes that research and
development (R&D) introduces the environmentally friendly technology
to reduce the environmental damages. New production of knowledge and
technological change can be increase through the active research and
development. New innovations and inventions can achieve due to the
research and development.
1.4.3. The Environmental Innovations and Market Size (GDP)
The positive dynamics in expansion in market size (GDP) is believed
to expand the innovative activities in the economies. One possible
reason for this expansion is industrial growth, which leads to invention
and innovations mostly by achieving economies of scale. But still direct
role of market size in innovations are not clear from the theory,
whether it help in increase in R&D, reduction in taxes, provision of
other incentives etc. Contrary, to the conventional economic growth
phenomenon, we are replicating it into green growth phenomenon. The
demand for the green products in the green markets size may contribute
in green R&D, imposition of green taxes, structure change at the
level of industries. This eventually may leads to green innovations. We
are assuming that the environmental technologies are developed by the
market size (GDP). New technologies support high volumes of goods and it
brings more companions in the economy and thus innovations are growing
fast. Large markets adopt more technological changes and market size is
also affected with new technologies. When the market size increases then
the environmental technologies enhance because when the GDP of one
economy rise then they are able to invest more in green technologies.
1.4.4. Environmental Innovations and Environmental Taxes
Taxes may have led the positive impact on environmental innovation
and economy. Environmental tax credits encourage innovative behavior and
the cleaner production techniques are more helpful in this sense
[Organisation for Economic Corporation and Development (2008)]. Korea is
badly affected by the urban air pollution. Government introduces the
emissions trading schemes and reduced the emissions by larger and
smaller emitters through the environmental taxation [OECD (2009e)].
Switzerland's federal government imposes the tax on volatile
organic compound (VOCs). Adaptation of technology and innovation is much
more in larger firms and less in smaller firms due to the financial and
information constraints [OECD (2009a)].
Sweden imposes the taxes on the emissions of nitrous oxide. New
technology of nitrous oxide emissions abatement required the new
innovations and innovation contribute ongoing emissions reductions and
continuing declines in abatement cost [OECD (2010)]. Air pollution from
motor vehicles produced the emissions and for sake of the emissions
reduction government imposed the taxes. Government gives their attention
to enhance the innovative and environment friendly technologies. In
nutshell, taxes have the positive effect on the environmental innovation
[OECD (2010)].
The environmental taxation has a positive impact on green
innovations because the government imposes the taxes on the polluters to
reduce the level of emissions and provide the clean environment to the
people. Specific environmental taxes e.g. CO2 taxes will support the
innovation in environmental/green technologies and also reduces the
activities of high pollution. When the pollutants paid the taxes then
increase the creation of new innovation, because the adaptation of
incentives in order to minimise the tax payments. In this result
potential innovation, production innovation, process innovation and
organisational innovation are also goes up. Transfer of innovations
among countries is due to the taxes in addition to the creation of
innovations. Taxation brings about a full range of innovations,
including new products and enhanced production techniques. The above
theoretical framework is depicted as:
[ILLUSTRATION OMITTED]
The graph clearly depicts the four important areas like IPRs,
R&D expenditures, market size measured by country GDP and
environmental taxations which ultimately has impact on green innovations
and these green innovations eventually leads to green growth.
1.5. Objectives of the Study
The implications of Intellectual Property Rights (IPRs) for
inventions and innovations are debatable in the literature. Although,
the literature [Maskus (2005); Archibugi and Filippettic (2010)] focuses
more on the positive role of the IPRs for innovations, while the
maturity level of the Industry/Finn structure are important considering
the implications of IPRs. One of our objectives of this study is chalk
out the role of IPRs in innovations in general and green innovations
particularly. To understand the process of eco-innovations this study
identifies three other direct determinants like research and development
(R&D), market size and environmental taxations. However we are
mainly focusing on environmental taxations whether the environmental
regimes works in green innovations. We don't have the data for
green R&D, therefore we are considering overall R&D expenditures
but its significance becomes less while linking it with green
innovations. But one of our objectives is to find the role of R&D in
green innovations.
Given the brief introduction of the problem stated earlier, this
study addresses the problem of IPRs, environmental taxation, and R&D
in green innovations in developed countries and would derive lessons for
Pakistan. The specific objectives are following:
(1) To find the impact of enforcement of Intellectual Property
Rights (IPRs) in environmental innovation.
(2) To assess the role of Research and Development (R&D) in
environmental innovation.
(3) To ascertain the role of environmental taxation in
environmental innovation.
(4) To derive the Policy implication from empirical results of the
study.
1.6. Organisation of the Work
Section 1 of this study includes definition of key terms, problem
and purpose statements. Section 2 describes data description and
methodology. Section 3 covers empirical estimations and results. Section
4 concludes the study with recommendations
2. DATA AND METHODOLOGY
2.1. Variables Specifications
2.1.1. Environmental Technology (Green Patents)
To know the action patterns and trends between technology the World
Intellectual Property Organisation (WIPO) present the data by field of
technology. Patent statics by technology field are based on the
"fractional counting" method. WIPO in June 2010 convert the
International Patent Classifications (IPC) symbol into 35 corresponding
fields of technology. In 2007 most applications are in computer field
technology, electrical machinery and telecommunication and due to these
technologies the highest annual growth rate was observed by 2003-2007.
On the other hand the OECD static database focus on the
environment-related technology because climate change is hot issue and
the environment related technologies plays an integral role in tackling
climate change. A total of 65 different IPC classes were identified that
dealt with purification of gases and emissions control. Three major
technologies were categories, which are improvement in engine, treating
pollutants produced before they are released into the atmosphere and
reduce evaporation emissions.
2.1.2. Intellectual Property Rights (IPRs)
A number of studies have attempted to measure IPRs protection
cross-nationally. Measurement of IPRs has become a critical issue for
international business, scholars and practitioners. In this regards Rapp
and Rozek's (1990s) attempted to quantify IPRs, they used patent
laws as a proxy for IPRs of 159 countries. Patent laws are marked on a
zero to five scale, where zero present a country with no patent laws and
five represent a country having laws consistent with the standards
established by the US chamber of commerce intellectual property task
force. Furthermore, Seyoum (1996) also used the US chamber of
commerce's minimum standard for his criteria. However, his 0-3
scales of IPRs protection components where constructed from survey sent
to IPRs practititioners. Seyoum constructed four variables such as
patents, copyrights, trademarks and trade secrets for his analysis.
Shrewood proposed a third measure of IPRs protection that combined the
personal interviews. The protection scores range from 0-103 and where
developed for eighteen countries. (4)
To properly tackle the issues of measurement Ginarate and Park
constructed IPRs index for 110 countries in the sample having data range
from 1960-2005. It ranges in values from zero to five. Higher values of
the index indicate stronger level of protection. In Rapp and Rozek and
Syoum did not include a component for enforcement in their study,
methods of differentiations is missing for example between
"inadequate laws" are "seriously flawed" laws or
between "generally good laws" and laws that are "fully
consistent" with the minimum standards. In Seyoum's study it
is unclear, on which criteria the raw data were reduced to a 0-103
scale. Sharewood's procedure is based on his experience. There
exist no set rules while judging how many points to subtract for
judicial independence, etc.
2.1.3. Research and Development (R&D)
Research and Development is one of the important components of
invention and innovations. In this context environment technologies are
largely depending on the R&D generally and green R&D expenditure
specifically. Research and development expenditures improve the new
innovative products and introduce the environment technology. R&D
expenditures would help in commercialisation of new technologies, create
new business and reduces the risk through the research and development.
This study hypothesised that the environment technology will efficiently
increase with the help of the overall research and development
expenditures. But limitation of green R&D expenditures data, we did
not use it.
2.1.4. Market Size (GDP)
Market size (GDP) is an important explanatory variable of the
development of environment technology. Market size is a measurement of
the total volume of a given market. When determining market size it is
very important to define the measurement as preciously as possible.
There are three ways to measure the market size such as bottom-up
approach, top-down approach and end-user purchases. It is assumed that
market size led the positive impact on development of environment
technology.
2.1.5. Environmental Taxation
Environmental taxation is considered the most important explanatory
variable of the development of environment technology. Environment
related taxes encourage innovations and then environment technologies
are developed. Benefits of the environment related taxes are when higher
pollution costs make it economically inviting to invest in the
development of new greener technologies. Taxes on pollution provide
cleaner incentives to polluters to reduce emissions and seek out the
cleaner alternatives. Environment related taxes can provide significant
incentives for innovation and these incentives make it attractive to
invest in research and development activities to develop environment
technology. Environmental taxation plays a key role in introducing and
developing the environment technology. Environment related taxes will
always lead to innovative and the adaptation of new technology and
processes. Taxes are the base of the new technology and innovations that
should make monitoring easier and most cost effective. Environment
related taxes introduce the full range of innovation as well as new
products and improved production techniques.
2.2. Data Description
This study included 11 developed countries namely Australia,
Austria, Canada, Finland, France, Germany, Japan, Korea, Sweden, United
Kingdom and United State based on the balanced data design for the
2000-2005. We faced many problems in the unbalanced data design for the
1995-2007. Therefore we used the balanced data in this study. Although,
the unbalanced data estimations are given at the annexure. The green
patents quantify the dependent variable of environmental technology. The
data on Environmental technology is taken from the OECD, Patent Database
(June 2008). The data on research and development (R&D) is taken
from OECD statistics catalogues. Market size (GDP) is an important
explanatory variable of the development of environment technology taken
from the World Development Indicators (2008). The data of environmental
taxation is also taken from OECD statistics catalogues.
2.3. Specification of the Model
The dependent variable is Environmental Technology and explanatory
variables are Intellectual Property Rights (IPRs), Research and
Development (R&D), Market size (GDP) and Environmental Taxation
through the Tax rate of Patrol and Tax rate of Diesel. The general
equation of this study is
Env.Tech = f[IPRs, R&D, Market size (GDP), Environmental Taxes
(TRP, TRD)] [(Env.Yech).sub.it]= [[alpha].sub.i] + [[beta].sub.1]
[(IPRs).sub.it] + [[beta].sub.2] [(R&D).sub.it] + [[beta].sub.3]
[(M.S).sub.it] + [[beta].sub.4] [(YRP).sub.it] + [[beta].sub.5]
[(TRP).sub.it] [V.sub.it] (i = 1, 2 ... N; t = 1,2 ... T) [V.sub.it] =
[[mu].sub.i] + [summation][W.sub.it]
Where:
ET = Environmental Technology, IPRs = Intellectual Property Rights,
R&D = Research and Development, M.S = Market size (GDP), TRP = Tax
rate of Patrol, TRD = Tax rate of Diesel and [[mu].sub.i] is
unobservable individual country specific effects and
[summation][w.sub.it] is other disturbances.
2.3.1. Pooled Least Square Estimation Techniques
Fixed Effect Model (FEM) or Random Effect Model (REM) is used on
the base of the balanced data design for 2000-2005. Hausman test is used
to approve the validity of FEM or REM. The reason for this time period
is that it contains a sizeable amount of data available for a large
cross section of countries. In pooled least square estimation two
techniques are used
* Fixed Effect Model (FEM)
* Random Effect Model (REM)
2.3.2. Fixed Effect Model (FEM)
Fixed Effect Model (FEM) using dummy variables is known as the
least square dummy variable models. FEM is appropriate in situation
where the specific intercept of countries may be correlated with one or
more regresses. Even if it is assumed that the under lying model is
pooled or random, the fixed effect estimators are always consistent. In
fixed effect the constant is treated as specific group. This means that
the model allows for different constants for each group. So the model is
[Y.sub.it] = [[alpha].sub.i] + [beta][x.sub.it] + [[mu].sub.it]
To understand this lets consider the following model [Asteriou, et
al. (2006)]
[Y.sub.it] = [[alpha].sub.i] + [[beta].sub.1][x.sub.1it] +
[[beta].sub.2][x.sub.2it] + [[beta].sub.3][x.sub.3it+....+] +
[[beta].sub.4][x.sub.4it] + [[mu].sub.i]
This can be rewritten in a matrix notation as:
[MATHEMATICAL EXPRESSION NOT REPRODUCIBLE IN ASCII]
Before assessing the validity of the fixed effects methods, to do
this the standard F-statics is used to check fixed effects against the
simple common constant OLS method.
[H.sub.0]: [a.sub.1] = [a.sub.2] = ... [a.sub.N]
F-statistics:
F = [([R.sup.2.sub.FE]-[R.sup.2.sub.CC])/(N - 1)]/(1
-[R.sub.2.sub.FE])/[(NT-N-K).sup.~] F (N-1, NT-N-K)
Where [R.sup.2.sub.FE] is the coefficient of determination of the
fixed effect model and [R.sup.2.sub.CC] is the coefficient of
determination of the common constant model. If F-statistics is greater
than the F-critical, then null hypothesis is rejected.
The Fixed Effects models may frequently have too many
cross-sectional units of observations requiring too many dummy variables
for their specification. Too, many dummy variables may sap the model of
sufficient number of degrees of freedom for adequately powerful
statistical tests. Moreover model with many such variables may be
plagued with multi-co linearity which increase the standard errors and
their by drains the model of statistical power to test parameters. If
these models contain variables that do not vary within the groups, the
parameters estimations may be precluded. Although the model residuals
are assumed to be normally distributed and zero mean at constant
variance, so there could easily be country specific heteroskedasticity
or autocorrelation overtime that would further plague estimations.
It ignores all explanatory variables that do not vary over time. It
means that it does not allow using other dummies in the model. This is
not useful, when it is required to consider such dummies. It considered
large number of degrees of freedom, which is a major cost. It makes it
very hard for any slowly changing explanatory variables to be included
in the model, because they will be highly collinear with the effects.
The fixed effects model controls for all time invariant differences
between countries, so the estimated coefficients of the fixed effect
models cannot be biased because of omitted time-invariant
characteristics like as culture, religion, gender, race, etc. one side
effect is that they cannot be used to investigate time-invariant causes
of the dependent variables.
Technically, time-invariant characteristics of the countries are
perfectly collinear with the cross-sections dummies. Substantively,
fixed effect models are design to study the causes of changes within a
cross-sectional. Time-invariant characteristics cannot cause such a
change, because it is constant for each person.
2.3.3. Random Effect Approach
The crucial distinction between Fixed and Random Effect is whether
the unobserved countries effect embodies elements that are correlated
with the regressors in the model, not whether these effects are
stochastic or not. Random effect model (REM) is consistent even if the
true model is the pooled estimator. If the dummy variables do in fact
represented a lack of knowledge about the model, why not express this
ignorance through the disturbance term. This is preciously the approach
suggested by the proponents so it is called Random Effect Model (REM).
The Random Effects Model
Original equation
[MATHEMATICAL EXPRESSION NOT REPRODUCIBLE IN ASCII]
Remember [[euro].sub.it] = [[lambda].sub.i] + [[mu].sub.it]
[[lambda].sub.i] is now a part of error term
This approach is appropriate if observation is representative of a
sample rather than the whole population. The Fixed Effect or LSDV
modeling can be expensive in terms of degrees of freedom, if we have
several cross-sectional units. Dummy variables in fact represent a lack
of knowledge about the true model. The proponents of random effects
model suggests to use the disturbance term [U.sub.it] in ordered to
capture the true effect.
Instead of treating [[alpha].sub.i] as fixed, now assume that it is
a random variable with a mean value of [a.sub.1] (no subscript here) and
the intercept value for an individual country can be expressed as:
[[alpha].sub.1i] = [[alpha].sub.1] + [[lambda].sub.ii=1,2,3,4 ...
N]
Composite error term [[euro].sub.it] consists of two components,
[[lambda].sub.i] which is the cross sectional or countries specific
error component and [U.sub.it], which is the combined time series and
cross-sectional error components.
[[euro].sub.it] = [[lambda].sub.i] + [[U.sub.it]
The random effects model therefore takes the following form:
[MATHEMATICAL EXPRESSION NOT REPRODUCIBLE IN ASCII]
Obvious disadvantage of the random effect approach is that one
should make specific assumption (i.e. country specific effects are
uncorrelated with the exogenous variables included in the model) about
the distribution of the random component. If the unobserved
group-specific effects are correlated with the explanatory variables,
then the estimates will be biased and inconsistent. An advantage of the
Random Effects is that you can include the time-invariant variable. In
the Fixed Effects model these variables are observed by the intercept.
Random Effects assumed that the entity's error term is not
correlated with the predictors, which allows for time-invariant
variables to play a role as explanatory variable.
In Random Effect you need to specify those countries
characteristics that may or may not influence the predictor variables.
The problem with this is that some variables may not be available
therefore leading to omitted variable bias in the model.
Disadvantages of the Random Effects are that one has to specify the
conditional density of [[mu].sub.i] given:
[X.sub.i] = ([X.sub.i], 1 ... [X.sub.i] t),
f([[mu].sub.i\][x.sub.i]),
While [[mu].sub.i] is unobservable. A common assumption is that f
([[mu].sub.i\][x.sub.i]) is identical to the marginal density
f([[mu].sub.i]). However, if the effects are correlated with [X.sub.it]
or if there is a fundamental difference among individuals units, i.e.,
conditional on [X.sub.it], [Y.sub.it], cannot be viewed as a random draw
from a common distribution, common Random Effect model is mis-specified
and the resulting estimator is biased.
The Fixed Effects model assumes that each country differs in its
intercept term (In FEM intercept vary across [[alpha].sub.i] of
cross-sectional units while in REF, intercept is constant), whereas the
Random Effects model assumes that each country differs in its error
term. When the panel data is balanced one might expect that the Fixed
Effects model will work better. In other cases, where the sample
contains limited observations of the existing cross-sectional units, the
random effect model might be more appropriate. The usefulness of fixed
effects model and random effects model depends upon the assumptions one
makes about the possible correlation between cross-sectional specific
error components [[lambda].sub.i] are constant and X's regressors.
If assumption is [[lambda].sub.i] and X's are uncorrelated, REM may
be appropriate. Whereas if [[lambda].sub.i] and X's are correlated
to the FEM may be appropriate. These are the two fundamental differences
in the two approaches.
In order to further investigate about whether fixed effects model
or random effects model is more useful, so called Hausman test is used.
Given a panel data model where Fixed effects would be appropriate the
Hausman tests investigates whether random effects estimation could be
almost as good. Hausman statistics may be viewed as a distance measure
between the Fixed Effects and the Random Effects estimators.
Hausman test uses the following test statistics:
[MATHEMATICAL EXPRESSION NOT REPRODUCIBLE IN ASCII]
For this test null hypothesis is;
[H.sub.o]: Random Effects model coefficients are consistent and
efficient.
[H.sub.i]: Random effects are inconsistent.
If the value of the Housman statistics is high, then the difference
between the estimates is significant, it rejects the null hypothesis and
the random effect model is inconsistent.
In contrast low value of the statistics implies that the random
effects estimator is more appropriate.
2.3.4 One Way or Two Way Error Component
[ILLUSTRATION OMITTED]
One way error components means, it includes Individual Effect and
Random Effect.
[[summation].sub.it] = [[lambda].sub.i] + [[mu.sub.it], Where the
[[lambda].sub.i] is the individual and [[mu].sub.it] is Random Error.
Two Way error component means, it includes the individual effect,
random effect and time effects.
[[summation].sub.it] = [[lambda].sub.i] + [[mu].sub.i] +
[[mu].sub.it]
Where [[lambda].sub.i], is individual effect and [[mu].sub.i] is
random error and [[mu].sub.it] is the time effects.
Two way error components cannot be applied to unbalanced data, and
the one way error components is applicable to the balanced or unbalanced
data. This study used the One Way Error Components. The One Way error
component is applied to the balanced data design for the 2000-2005.
3. EMPIRICAL ESTIMATION AND RESULTS
3.1. Empirical Findings
In order to estimate the pooled least square estimation techniques
of fixed and random effect, we are going to check the stationarity of
panel data by employing panel unit root test introduced by
Phillips-Perron Fisher (Fisher-PP) Unit Root Test. It considers the
Kernel (Bartlett) method to correct for autocorrelation. We also check
for the individual intercept to include individual fixed effects,
individual trend and intercept to include both the fixed effects and
trend, finally none to include no regressors. These results are
exhibited in Table 1.
The Table l, clearly depicting that each specification of the panel
unit root test (individual intercept, individual trend and intercept and
none) rejects the null of unit root hypothesis for all the series that
is combined tax on petrol and diesel (CTRit), the tax rate on petrol
(TRPit), the green technology (GreenTit), are stationary at i.e. I (0),
except the GDP I (1). The remaining two pool series i.e. tax rate on
diesel (TRDit) and intellectual property right index (IPRit) are
non-stationary. On the whole when we are using the combined tax rate we
can say that the series are stationary, therefore, we proceeds for the
pooled least square estimation techniques of fixed and random effects
method.
The Pooled Least Square (Balanced or Unbalanced) Fixed Effect and
Random Effect Models are used to estimate equation and the results are
presented in Table 2 and Table 3 at the end of the chapter. We are not
considering the unbalanced estimation the reason is that the data is not
frequently available for all years. Therefore, we used the balanced data
and the results are highly significant in the balanced data. Since,
there are no significant differences in the results of the above
mentioned results. Their magnitudes are different but their signs are
same, therefore the results have been interpreted in a combined manner.
But here focus on the Fixed Effect because the results are highly
significant in the Fixed Effect.
The individual results of the tax rate on patrol and tax rate on
diesel are put in the Annex 1 and Annex 2. Whereas, the results of the
combine tax rate are highly significant and positive as compared to
individual results of the tax rate on patrol and diesel. The preliminary
results show that the coefficients of the most of the standard
explanatory variables carry the expected signs and are statistically
significant.
Fixed Effect is shown clearly in Table 2. It further depict that
combine tax rate (CTRit) which is defined as the tax rate on patrol and
tax rate on diesel, carries the expected sign and is highly significant.
The finding shows that the combined tax rates have the positive
relationship with the green technology and 86.76 percent green
technology is increased due to the combine tax rate. One reason for this
significant relationship is that if there is tax imposed on polluters
then there would be the level of emissions and activities of high
pollution. Taxes on pollution provide clear incentives to polluters to
reduce emissions and seek out cleaner alternatives. By placing a direct
cost on environmental damage, profit maximising firms have increased
incentives to economise on its use, compared to other environmental
instruments, such as regulations concerning emission intensities or
technology loss environment related taxation, as it encourages both the
lowest cost abatement across polluters and provide incentives for
abatement at each unit of pollution. When the pollutants pay taxes then
the creation of the innovation is came because of the adaptation of
incentives in order to minimise the tax payments and in this result
potential innovation, production innovation, process innovation and
organisational innovation are came. These incentives make it
commercially attractive to invest in R&D activities to develop
technologies. Taxes equate the marginal damages from pollution with the
marginal cost of pollution abatement. Taxations bring about a full range
of innovation, including new products and enhanced production
techniques. Faxes on pollution provide cleaner incentives to polluters
to reduce emissions and seek out the cleaner alternatives.
Another reason is that taxes on motor vehicles are major source of
revenue for 11 developed countries government and taxes are the base of
new technology and innovation that should make monitoring easier and
most cost effective. Taxes lower the prices of permits but recover some
of the wind fuel gains that firms receive by not having to buy their
permits at auction. The scope of the expanded use of the environmentally
related taxes in 11 countries is great, especially in addressing climate
change. This result is corresponding with the (Organisation for Economic
Cooperation and Development, 2008). [OECD (2009); OECD (2009a) and OECD
(2010)].
This study finds that for developed countries with the
strengthening of IPR regime, the green technology is declining. The
coefficient associated with IPR indicates that with a one unit increase
(more strengthening) in the IPR index, the green technology declines by
11.34 percent. It means that the empirical results do not support
positive relation between IPR and green technology in developed
countries. The possible reason for this negative relationship might be
the structure of the industries in the developed countries. Furthermore,
enforcement of IPRs would not affect the green innovations in these
industries. The structure of these industries has reached at the mature
level and changing structure would cost those more instead of converting
in to green innovations. Moreover, the IPRs enforcement index in these
countries almost reached at the maximum of 5 (means full enforcement).
Therefore, further IPRs enforcement wouldn't work. The Clean
Development Mechanism (CDM) also verifies these study findings that the
developed countries instead of changing their structure towards green
technologies they are purchasing carbon credits from the developing
countries.
Research and Development is defined as creating the new production
of knowledge and technological change, it is significant and carry the
expected signs. The findings show that there is a positive relation in
R&D and green technology: green technologies are increase 1.31
percent due to the R&D. The coefficient of R&D indicates that as
a result of 1 percent increase in the R&D, the green technologies
increase by the 1.31 percent. The reason of this significant
relationship is that new innovations and inventions are overcome due to
the R&D. New R&D produces the higher quality of goods; create
the new production of knowledge, technological change and higher degrees
of technology transfer. R&D expenditure helps in commercialisation
of new technologies, create new business and reduce the risk through the
R&D. Active R&D reduces the green house gas emissions and energy
efficient technologies. This result is subsequent with the [William
(2006); David and Roger Bate (2010)].
Market Size (GDP) has a significant impact on the green
technologies of the Developed countries. In this regard the results are
highly significant. The coefficient of the GDP indicates that as a
result of 1 percent increase in GDP the green technologies increases by
the 0.0209 percent. The empirical analysis favors the positive role of
GDP in green technologies. When GDP increase then the Purchasing Power
Parities increase and over the time Government realise about the
environmental degradation and then there is progressive increase the
green taxes. When taxes are levied from the polluters then polluters
favor the green technologies rather than the taxes. This result is
corresponding with the [David and Roger Bate (2010); Maskaus (2005);
Thomas (2006); Steiner (2009)].
3.2. Econometric Tests
We applied the Hausman test to further investigate about whether
fixed effects model or random effects model is more useful. The Hausman
test favored the null of Fixed Effect Technique instead of alternative
of Random Effect Technique. Also, apply Durbin-Watson d test to check
for autocorrelation in time series and cross sectional data to identify
the autocorrelation problem if any. This test assumes inclusion of
intercept in regression model and there are no missing observations. In
this case, the validity of this test is not useful to interpret for
balance panel data. The value of D.W. test is irrelevant in case of
small time series which in this case is only five years, with eleven
cross sections. However, we are considering this test to fulfill the
basic requirements. Similarly, the first assumption violates the
applicability of Constant Coefficient Method. However, D.W. d statistic
value can be usefully interpreted for balanced panel data (Fixed and
Random effects). The value of the Durbin-Watson Statics is closed to 2
if the errors are uncorrelated. The values of D.W. Stat for balanced
data (2000-2005) are 0.034. We already explained when the time period is
short and there is no need to take the lags because the minimum values
are not matter in this case.
White General Hetroscedasticity, White Heteroscedasticity Variance
and Standard Error methods were applied respectively to check and
correct the problem of Heteroscedasticity, The usefulness of the White
Heteroscedasticity Variance and Standard Error on Weighted Least Square
(WLS) is that it does not assume, rather determines variance
([[??].sub.i.sup.2]). The problem of Hetroscedasticity is more common in
cross sectional data than in time series data, because it deals with
members of cross country population at a given point of time, such as
individual consumers, or their families, firms, industries, or
geographical subdivisions like state, country, city etc. [Janjua and
Samad (2007)]. Therefore, we explained the results of Fixed Effect
estimations
4. CONCLUSIONS AND POLICY IMPLICATION
It is an open secret that the Environmental technology is perceived
as an important source of reducing the emissions and to improve the
efficiency in market(s). Such technologies play a vital role in tackling
with the issues like climate change. Moreover, Green environment
technologies focus on the innovation that resultants in minimising the
degradation of environment; reduce the green house gas emissions,
improve the health, conserve the use of natural resources and also
promotes the use of both renewable and non-renewable resources. Such
innovations, also reduces the cost of materials, cost of production,
increase the rates of production and attractiveness of products in the
market place.
Our research has also proved that the promotion of environment
technology and eco-innovation provides many benefits for business;
fostering innovation, cutting production cost, creating jobs, reducing
pressures on the environment and encourage competitiveness. Limiting the
concentration of green house gases in the atmosphere is largely a major
concern of the technology innovation.
The empirical results do not support the positive relation between
the IPRs and green technologies in developed countries. Because the
enforcement of IPRs does not affect the green innovations, as the
organisation of these industries reached at mature level and changing
structure would cost those more instead of converting into green
innovations. (6) Moreover, the IPRs enforcement index in these countries
almost reached at the maximum of 5 (7) (means full enforcement). Hence,
the developed countries, instead of changing their structure towards
green technology, are purchasing carbon credits from the developing
countries. (8) Nevertheless, our literature review of IPRs has a
positive impact on eco-innovation, but this very study shows a negative
relation. The possible reason for this negative relationship might be
the structure of the industries in the developed countries. Furthermore,
the enforcement of IPRs would not affect the green innovations in these
industries. Because, the structure of these industries reached at the
mature level and changing structure would cost those more instead of
converting into green innovations. The Clean Development Mechanism (CDM)
also verifies the said study.
Research and Development (R&D) plays positive and increasingly
significant role in innovation and environmental technologies.
Emphasising R&D introduces the environment friendly technologies to
reduce the environmental damages. Environment technologies are largely
depending on R&D generally and green R&D. R&D expenditure
improves the new innovative products and initiates the environment
technologies. R&D expenditure would help in commercialisation of new
technologies, create new business and reduce the environment
degradation. R&D resultants in the production of environment
friendly and higher quality of goods, that ensures sustainable
development. Such products would also be helpful in minimising pollution
and minimising its other externalities.
Environmental taxation also plays a key role in introducing and
developing the environmental technologies because environment related
tax leads to innovation and adaptation of new technologies and
processes, both at micro and macro level. Taxes generate and huge income
for the government which would be used to invest in the eco-technology.
Environment related taxes introduce the full range of innovation, new
products and new production techniques. Such taxes also provide
significant incentives, both for consumers and producers that would
trigger the revolution and innovative and environment friendly ideas in
the field of science and technology.
The Important Policy Implications Are
* Management of Intellectual Property Rights (IPR) based on
eco-innovation.
* National intellectual property legislation should be updated and
refined and imposed.
* The role of ministries (environment), organisations/institutions,
and Word Intellectual Property Organisation (WIPO) should emphasise on
the role of IPR and Green technology development.
* R&D base should be strengthened, which will encourage
innovative efforts to invent environment friendly products.
* An effective environmental taxation needs to be introducing
keeping in mind the willingness to pay of the individuals of the
proposed community.
ANNEX-1
Fixed Effect
Dependent Variable: Green Technology
Method: Pooled EGLS (Cross-section weights)
Total Pool (balanced) observations: 726
White cross-section standard errors & covariance (d.f. corrected)
Variables Coefficient St. Error t-Statistic Prob.
C 3.6618 0.1029 35.5731 0.0000
IPR -12.8528 0.7805 -16.4668 0.0000
R&D 4.7400 0.7232 6.5537 0.0000
GDP 0.0207 0.0007 28.4744 0.0000
TRP 85.4756 22.4118 3.8138 0.0001
TRD 86.5914 13.3584 6.4821 0.0000
R-Squared 0.73
Adjusted R-Squared 0.72
F-Statistic 131.1818
F-Statistic (Prob.) 0.0000
Durbin-Watson stat 0.3957
ANNEX-II
Random Effect
Dependent Variable: Green Technology
Method: Pooled EGLS (Cross-section weights)
Total Pool (balanced) observations: 726
White cross-section standard errors & covariance (d.f. corrected)
Variables Coefficient St. Error t-Statistic Prob.
C 0.0446 0.5349 0.0835 0.9335
IPR -34.0442 2.0208 -16.8464 0.0000
R&D -2.3497 1.2967 -1.8120 0.0704
GDP 0.0346 0.0013 25.5437 0.0000
TRP 468.6140 55.5425 8.4370 0.0000
TRD -15.6808 62.1877 -0.2521 0.8010
R-Squared 0.60
Adjusted R-Squared 0.59
F-Statistic 216.0555
F-Statistic (Prob.) 0.0000
Durbin-Watson stat 0.2655
REFERENCES
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Eco-innovation. The Case of the Technology Transfer and Climate Change
in a Post-2012 Policy Framework. (OECD Environment Working Paper).
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(1) United Nation and Economic Commissions &Asia Pacific
(UNESCAP).
(2) http://www.gpnm.org/e/articles/Definition-of-Green-Technology-by-KETTHA-Ministry-of-Energy-Green-Technology-and-Water-a5.html 6 Oct
2010.
(3) WIPO conference on Innovation and Climate Change.
(4) Ghulam Samad "Intellectual Property Rights and Economic
Growth" 2007, pp. 711-722.
(6) This view is discussed by Dr Zahiruddin Khan, IESE NUST in
International conference on Green Technology organised by COMSTECH.
(7) Ghulam Samad, "Intellectual Property Rights and Economic
Growth" 2007.
(8) CDM Mechanism.
Ghulam Samad <ghulamsamad@hotmail.com> is Research Economist
at the Pakistan Institute of Development Economics, Islamabad. Rabia
Manzoor <rabia_ch@live.com> is Research Associate at the
Sustainable Development Policy Institute (SDPI), Islamabad.
Table 1
Panel Unit Root Tests
Null: Unit Root (assuming individual unit root process)
Phillips-Perron Fisher Unit
Root Test (Chi-Square)
Pool Individual Individual None
Series Intercept Trend and
Intercept
CTRit 53.270 50.290 264.777
(0.0002) (0.0005) (0.0000)
TRPit 120.000 279.730 578.887
(0.0000) (0.0000) (0.0000)
TRDit 2.772 2.772 2.772
(1.000) (1.000) (1.000)
GreenTit 41.06 29.11 68.89
(0.0081) (0.1415) (0.0000)
R&D it 180.36 165.95 1200.54
(0.0000) (0.0000) (0.0000)
GDPit (1st 30.031 24.4000 47.711
Difference) (0.1177) (0.3266) (0.0012)
IPR it 12.476 12.476 12.476
(0.9467) (0.9467) (0.9467)
Figures in parentheses are representing the P-values.
Table 2
Fixed Effect
Dependent Variable: Green Technology
Method: Pooled EGLS (Cross-section weights)
Total Pool (balanced) observations: 726
White cross-section standard errors and covariance (d.f, corrected)
Variables Coefficient St. Error t-Statistic Prob.
C 3.7545 0.0959 39.1118 0.0000
CTR 86.7693 8.6120 10.0753 0.0000
IPR -11.3401 0.8387 -13.5195 0.0000
R&D 1.3198 0.6414 2.0576 0.0400
GDP 0.0209 0.0006 32.4154 0.0000
R-Squared 0.69
Adjusted R-Squared 0.69
F-Statistic 117.6160
F-Statistic (Prob.) 0.0000
Durbin-Watson stat 0.3867
Table 3
Random Effect
Dependent Variable: Green Technology
Method: Pooled EGLS (Cross-section weights)
Total Pool (balanced) observations: 726
White cross-section standard errors and covariance (d.f. corrected)
Variables Coefficient St. Error t-Statistic Prob.
C 0.0473 0.3177 0.1489 0.8816
CTR 253.5789 4.8319 52.4799 0.0000
IPR -40.9286 4.6384 -8.8238 0.0000
R&D 15.9355 6.9019 2.3088 0.0212
GDP 0.0326 0.0011 28.5715 0.0000
R-Squared 0.59
Adjusted R-Squared 0.58
F-Statistic 259.7878
F-Statistic (Prob.) 0.0000
Durbin-Watson stat 0.2498