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Why is the restoration of the natural environment of biodiverse ecosystems not recognized everywhere as one of the priority elements of the green transformation of the economy?
Should the restoration of the natural environment of biodiverse ecosystems, including highly biodiverse forest ecosystems in post-industrial and other areas degraded by unsustainable human activities be recognized as one of the priority elements of the green transformation of the economy?
Why included in Goal 15 (of the UN's 17 Sustainable Development Goals) is the restoration of the natural environment of biodiverse ecosystems in post-industrial areas, the restoration of highly biodiverse forest ecosystems, the development of reforestation programs, which should be implemented on a large scale already by 2020 (Task 15.1. included in the 2030 Agenda for Sustainable Development: By 2020, ensure the protection, restoration and sustainable use of terrestrial and inland freshwater ecosystems and other ecosystems, particularly forests, wetlands and drylands, and mountains, in accordance with international commitments). has still not been implemented in some countries?
Ongoing research shows that included in Goal 15 (out of the UN's 17 Sustainable Development Goals) is the restoration of the natural environment of biodiverse ecosystems in post-industrial areas, the restoration of highly biodiverse forest ecosystems, the development of afforestation programs, which should already be implemented on a large scale by 2020 (Task 15.1. included in the 2030 Agenda for Sustainable Development: By 2020, ensure the protection, restoration and sustainable use of terrestrial and inland freshwater ecosystems and other ecosystems, particularly forests, wetlands and drylands, and mountains, in accordance with international commitments). has still not been implemented in some countries. In some countries, in recent years, there are still many post-industrial areas, including mining spoil heaps, that have not been developed in accordance with the principles of sustainable development, i.e. restoration of the natural environment has not been undertaken. In addition, in some countries, still instead of sustainable forest management consisting of strict protection of old-growth, natural highly biodiverse forest ecosystems, restoration of biodiverse forest ecosystems referring to the natural ones occurring for thousands of years in a specific area characterized by a specific mix of natural and climatic conditions, industrial cultivation of only some tree species for industrial cutting is carried out, and predatory pseudo forest management consisting of cutting all trees in a specific area is carried out, including cutting down old-growth forests and by the way destroying entire biodiverse ecosystems, which also results in accelerated degradation, soil barrenness, deterioration of water retention and local microclimate. On the other hand, it has been widely known for many years on the basis of the results of thousands of research works that restoration of the natural environment, including biodiverse forest ecosystems, increases the scale of sustainability in terms of human-biosphere, climate and biodiversity relations. In turn, the restoration of the natural environment in post-industrial and other areas degraded by unsustainable human activity increases the areas of the biosphere and reduces the scale of the negative effects of civilizational unsustainable human activity, including reducing the scale of environmental pollution and reducing the accumulation of greenhouse gases in the atmosphere. The effect is to slow down the progressive greenhouse effect and thus reduce the scale of global warming. Reducing the scale and slowing down the progressive process of global warming generates a reduction in the scale of the negative effects of the ongoing climate change, i.e. a reduction in the scale and frequency of weather anomalies and climatic disasters, including, above all, the increasingly severe periods of drought covering more and more land areas, in addition to the yearly occurrence of higher and higher summer temperatures, increasingly severe shortages of drinking water and/or increasingly violent storms with torrential rains and floods. Therefore, the restoration of the natural environment in areas degraded by the development of industry, ongoing mining activities or unsustainable agriculture in the industrial formula, including the development of afforestation programs, restoration of biodiverse forest ecosystems contributes to improving the local microclimate, improves water retention processes, slows down the processes of soil barrenness and/or reverses these processes, contributes to the restoration of highly fertile and biodiverse microbial soils, results in increasing the scale of ecological and climatic sustainability, increases the scale of resilience of the planet's highly biodiverse natural ecosystems and/or flexibility to adapt to a changing climate, and improves livelihoods for humans as well. Therefore, taking into account the above-mentioned great positive qualities of the processes of restoration of the natural natural environment, including biodiverse forest ecosystems then, in parallel, the scale of strict nature conservation should be increased, including increasing the areas of natural ecosystems, including natural natural ecosystems and those being restored. In this way, the amount of greenhouse gases accumulating in the atmosphere will increase more slowly, and thus the process of global warming, which has been accelerating over the past several decades, can be slowed down. In view of the above, due to the high level of relevance of the process of restoration of the natural environment, reclamation of areas of natural ecosystems devastated by man, protection of highly biodiverse natural ecosystems for the climate and biosphere of the planet and also for future generations of people, restoration of the natural environment, including biodiverse forest ecosystems in post-industrial and other areas degraded by unsustainable human activities should be considered one of the priority elements of the green transformation of the economy. Implemented fully and seriously, the green transformation of the economy, in which an important role is played by pro-climate, pro-environmental, pro-biodiversity and thus realistically also pro-social policies, should also fully take into account the UN 17 Sustainable Development Goals. Unfortunately, this is still not practiced in all parts of the world.
I am conducting research on this issue. I have included the conclusions of my research in the following article:
IMPLEMENTATION OF THE PRINCIPLES OF SUSTAINABLE ECONOMY DEVELOPMENT AS A KEY ELEMENT OF THE PRO-ECOLOGICAL TRANSFORMATION OF THE ECONOMY TOWARDS GREEN ECONOMY AND CIRCULAR ECONOMY
In view of the above, I address the following question to the esteemed community of scientists and researchers:
Why included in Goal 15 (out of the UN's 17 Sustainable Development Goals) is the restoration of the natural environment of biodiverse ecosystems in post-industrial areas, the restoration of highly biodiverse forest ecosystems, the development of reforestation programs, which should be implemented on a large scale already by 2020 (Task 15.1. included in the 2030 Agenda for Sustainable Development: By 2020, ensure the protection, restoration and sustainable use of terrestrial and inland freshwater ecosystems and other ecosystems, particularly forests, wetlands and drylands, and mountains, in accordance with international commitments). still not implemented in some countries?
Should the restoration of the natural environment of biodiverse ecosystems, including highly biodiverse forest ecosystems in post-industrial and other areas degraded by unsustainable human activities be considered one of the priority elements of the green transformation of the economy?
Why is the restoration of the natural environment of biodiverse ecosystems not recognized everywhere as one of the priority elements of the green transformation of the economy?
What do you think about this topic?
What is your opinion on this issue?
Please answer,
I invite everyone to join the discussion,
Thank you very much,
Regards,
Best wishes,
Dariusz Prokopowicz
The above text is entirely my own work written by me on the basis of my research.
In writing this text, I did not use other sources or automatic text generation systems.
Copyright by Dariusz Prokopowicz
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The climate crisis is multifaceted with the environmental crisis. Accordingly, the protection of nature, the biosphere, the biodiversity of the planet's natural ecosystems should, like climate protection, be universally recognized as a key strategic goal of green economic transformation, scaling up the implementation of the Sustainable Development Goals and building a sustainable, zero-carbon, green circular economy.
To support my thesis, I give the results of my research in the following publication:
IMPLEMENTATION OF THE PRINCIPLES OF SUSTAINABLE ECONOMY DEVELOPMENT AS A KEY ELEMENT OF THE PRO-ECOLOGICAL TRANSFORMATION OF THE ECONOMY TOWARDS GREEN ECONOMY AND CIRCULAR ECONOMY
What do you think about this?
What is your opinion on this topic?
Best regards,
Dariusz Prokopowicz
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Can the non-implementation of electoral promises on the issues of sustainable economic development, green transformation of the economy, increasing pro-climate and pro-environmental policy measures by the political options winning the elections be considered as antisocial activities and not in compliance with basic human rights and the Constitution?
In recent years, more and more different political options during election campaigns before parliamentary and other political elections have added to their election slogans the issues of sustainable economic development, green transformation of the economy, increasing pro-climate and pro-environmental policy measures, including a significant increase in the development of renewable energy sources, decarbonization of industry, development of sustainable organic agriculture, sustainable energy-efficient construction, electromobility, recycling, development of sustainable tourism, development of urban agglomerations in accordance with the concept of green smart city, significant increase in the scale of reclamation of natural environments in areas degraded by industrial development, increase in the scale of protection of biodiverse natural ecosystems, natural forest ecosystems, increase in the scale of reforestation and other aspects of a sustainable green circular economy, and after winning the elections, they only slightly implement their election promises to citizens, or do not implement these promises at all. Since the scale of this phenomenon is growing so the importance of the discussions held in the issues of not fulfilling election promises on the issues of sustainable economic development, green transformation of the economy, increasing pro-climate and pro-environmental policy measures by the political options winning the elections is also increasing. When this kind of situation is repeated repeatedly in a certain country then citizens begin to consider the possibility of recognizing this kind of unreliable political activity as antisocial and perhaps also not in accordance with basic human rights and the Constitution.
I am conducting research on this issue. I have included the conclusions of my research in the following article:
I invite you to discuss this important topic for the future of the planet's biosphere and climate.
In view of the above, I address the following question to the esteemed community of scientists and researchers:
Can the non-implementation of election promises on the issues of sustainable economic development, green transformation of the economy, increasing pro-climate and pro-environmental policy measures by the political options winning the elections be considered as antisocial activities and not in compliance with basic human rights and the Constitution?
Can the non-fulfillment of election promises by election-winning political options be considered antisocial activity?
What do you think about this topic?
What is your opinion on this issue?
Please answer,
I invite everyone to join the discussion,
Thank you very much,
Best regards,
Dariusz Prokopowicz
The above text is entirely my own work written by me on the basis of my research.
In writing this text, I did not use other sources or automatic text generation systems.
Copyright by Dariusz Prokopowicz
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Labeling the non-fulfillment of election promises by winning political options as "antisocial activity" might be too strong a characterization. It's more commonly seen as a breach of trust or a failure of accountability. While it can lead to disillusionment and frustration among citizens, categorizing it as antisocial activity suggests intentional harm or disruption to society, which may not always be the case.
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In what aspects, carried out through the implementation of the principles of sustainable, green closed-loop economics, does climate protection connect with the protection of the biosphere and biodiversity of the planet's natural ecosystems?
In what aspects does the reduction of greenhouse gas emissions and the implementation of the principles of green closed-loop economics and pro-environmental sustainable economic development and thus carried out for the needs of future generations of people, climate protection combines with the protection of the biosphere and biodiversity of the natural ecosystems of the planet?
In my opinion, climate protection combines with the protection of the biosphere and the biodiversity of the planet's natural ecosystems in many ways. Many issues of climate protection also affect the issue of the biosphere and biodiversity of the natural ecosystems of the planet. On the other hand, by taking care of the state of nature, protecting the natural environment, strengthening systems for protecting the biosphere, and improving solutions for protecting the biodiversity of the planet's natural ecosystems, we also contribute to protecting the planet's climate. Many issues in the aforementioned issues of protecting the planet's climate, biosphere and biodiversity of the planet's natural ecosystems are interrelated. For example, increasing the scale of reforestation, restoration of natural ecosystems, restoration of biodiverse forest ecosystems both constitute an important element in the protection of nature, the biosphere and biodiversity of flora and fauna but are also an important element in the protection of the climate, both the microclimate locally and the climate globally. In recent times, the change in trends occurring in many urban areas from the ubiquitous years ago so-called concretization, that is, the removal of green areas, the creation of wide sidewalks, concrete squares, asphalt surfaces, etc. to greening, creation of new city parks, reduction of concretes, reduction of areas covered with concrete and asphalt, creation of additional green areas, lawns, flower meadows, pocket parks, etc. is also an important element of pro-climate and at the same time pro-environmental, sustainable economic development and a feature of a modern city developing in accordance with the green smart city concept. Also, the replacement of unsustainable, implemented according to the formula of intensive, production agriculture with sustainable organic agriculture at the same time fits into the pro-environmental and pro-climate policy. Conservation of water resources, implementation of water efficiency systems, creation of rainwater catchment facilities for use in agriculture and irrigation of parks and home gardens is also an important element of sustainable development, green closed-loop economics and protection of both the biosphere and the planet's climate. Also, the creation of new landscape parks, conservation areas, natural national parks is an important element in the protection of the biosphere, biodiversity and the planet's climate.
Key aspects of the negative effects of the ongoing process of global warming and the associated necessary acceleration of the processes of green transformation of the economy in order to decarbonize the economy, slow down the process of global warming, protect the climate, biosphere and biodiversity of natural ecosystems of the planet I described in the article:
IMPLEMENTATION OF THE PRINCIPLES OF SUSTAINABLE ECONOMY DEVELOPMENT AS A KEY ELEMENT OF THE PRO-ECOLOGICAL TRANSFORMATION OF THE ECONOMY TOWARDS GREEN ECONOMY AND CIRCULAR ECONOMY
In view of the above, I address the following question to the esteemed community of scientists and researchers:
In what aspects does the reduction of greenhouse gas emissions and the implementation of the principles of the green circular economy and pro-environmental sustainable economic development, and thus carried out for the needs of future generations of people, climate protection is combined with the protection of the biosphere and biodiversity of the natural ecosystems of the planet?
In what aspects, carried out through the implementation of the principles of sustainable, green closed-loop economics, does climate protection connect with the protection of the biosphere and biodiversity of the planet's natural ecosystems?
How does climate protection connect with the protection of the biosphere and biodiversity of the planet's natural ecosystems?
What do you think about this topic?
What is your opinion on this issue?
Please answer,
I invite everyone to join the discussion,
Thank you very much,
Best regards,
Dariusz Prokopowicz
The above text is entirely my own work written by me on the basis of my research.
In writing this text, I did not use other sources or automatic text generation systems.
Copyright by Dariusz Prokopowicz
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Dear Prof. Prokopowicz!
You raised an excellent but difficult problem to address. I did my best to find a case study on this matter. The one below represents the strategy of Sweden:
Felton, A., Belyazid, S., Eggers, J. et al. Climate change adaptation and mitigation strategies for production forests: Trade-offs, synergies, and uncertainties in biodiversity and ecosystem services delivery in Northern Europe. Ambio 53, 1–16 (2024). https://doi.org/10.1007/s13280-023-01909-1, Open access:
Yours sincerely, Bulcsu Szekely
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On the successional processes, as we know, initially there is no plant and by the time plants are gradually coming into the ecosystem through various ways. On the restoration project, succession may get faster by artificial planting. Planting tree may cut some successional steps and bring the ecosystem directly to the late stage. However, I am curious, is it important for planting grass and shrub before planting tree? it seems that the successional process is not as fast as planting trees directly, but I am wondering with the effectiveness. 
If any of you can explain about it, I would appreciate it.
Bests
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From my experience as practitioner, key factors are also the starting condition and the resources available to control weeds in the planted area.
For example, planting native grasses into a ground layer of exotic grasses will require a large workforce to complete required ongoing exotic grass control
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How can new technologies including Big Data Analytics, artificial intelligence and other emerging technologies Industry 4.0/5.0 help restore biodiverse natural forest ecosystems?
The restoration of biodiverse natural forest ecosystems in civilization-degraded areas, post-industrial areas, post-mining spoil heap areas, post-agricultural areas characterized by permanent drought and depleted soil, areas increasingly exposed to the negative effects of climate change, including global warming, etc., is one of several key elements of restoration. is one of several key elements in the reclamation of the natural environment, and thus also one of the main factors in the green transformation of the economy, building a sustainable closed-loop economy, achieving the goals of sustainable development, protecting the planet's biosphere, biodiversity and climate. The technological advances taking place should help smoothly carry out the green transformation of the economy, protecting nature, biodiversity and the planet's climate. Accordingly, new technologies, including Big Data Analytics, artificial intelligence and other Industry 4.0/5.0 technologies, should be used in the restoration of biodiverse natural forest ecosystems. However, the aforementioned new technologies, including Big Data Analytics technology, artificial intelligence and other Industry 4.0/5.0 technologies, especially when they are used in large computerized data centers then consume large amounts of energy. Therefore, in order for the process of using new technologies, including Big Data Analytics, artificial intelligence and other technologies that consume large amounts of energy when they are used in large data centers to fit in with the trend of green transformation of the economy and the realization of sustainable development goals, they should be powered by electricity generated from renewable and zero-carbon energy sources.
I described the key issues of opportunities and threats to the development of artificial intelligence technology in my article below:
OPPORTUNITIES AND THREATS TO THE DEVELOPMENT OF ARTIFICIAL INTELLIGENCE APPLICATIONS AND THE NEED FOR NORMATIVE REGULATION OF THIS DEVELOPMENT
In view of the above, I address the following question to the esteemed community of scientists and researchers:
How can new technologies including Big Data Analytics, artificial intelligence and other Industry 4.0/5.0 technologies help in the restoration of biodiverse natural forest ecosystems?
How can new technologies including artificial intelligence and other new technologies help restore biodiverse natural forest ecosystems?
What do you think on this topic?
What is your opinion on this issue?
Please answer,
I invite everyone to join the discussion,
Thank you very much,
Best regards,
Dariusz Prokopowicz
The above text is entirely my own work written by me on the basis of my research.
In writing this text I did not use other sources or automatic text generation systems.
Copyright by Dariusz Prokopowicz
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New technologies like Big Data Analytics and AI can aid in monitoring and managing natural forest ecosystems. They enable real-time data collection, analysis, and predictive modeling, helping to identify patterns, assess biodiversity, and detect potential threats such as deforestation or invasive species. By leveraging these technologies, conservation efforts can become more proactive and effective in restoring and preserving biodiverse natural forest ecosystems.
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With the smooth green transformation of the economy, building a green, sustainable, zero-carbon closed-loop economy, and with the large-scale implementation of new green technologies and zero-carbon energy eco-innovations, etc., will it be possible in the future to restore the biodiversity of natural ecosystems previously destroyed by man, made by the development of civilization the loss of biodiversity of natural ecosystems?
In recent years, large-scale green investment projects have been launched in some countries, which are being carried out as part of the green transformation of the economy to build a sustainable, green, zero-carbon zero-growth and closed-loop economy. The essence of the ongoing large-scale implementation of the aforementioned processes in some regions of the world is to carry out a pro-environmental and pro-climate transformation of the classic growth, brown, linear economy of excess into a sustainable, green, zero-carbon zero-growth and closed-loop economy. One of the economic regions of the world where these issues have been prioritized, ambitious plans have been set out to smoothly carry out the green transformation of the economy is the European Union. One of the many components of the green transformation of the economy is the large-scale creation and implementation of new green technologies and eco-innovations. Well, in recent years, many new green technologies and eco-innovations are being created in the framework of clean emission-free energy, biodegradable materials, electromobility, cleaning up the polluted environment, increasing the scale of recycling, economical use of natural resources, conservation of clean water resources, restoration of green areas in cities, reforestation of wasteland and civilization-degraded areas, and so on. If such processes of efficiently carried out green transformation of the economy are carried out on a large scale in all countries of the world, there is still a chance to significantly slow down the progressive process of global warming and save the net from the projected global climate catastrophe. Therefore, the chance to save at least in part the remaining biosphere of the planet, to save the biodiversity of the natural ecosystems of the planet, i.e. the greatest value of the planet Earth that has been created by the many millions of years of evolution of life on the planet, increases. The issue of conservation, protecting the planet's biosphere and saving the remaining biodiversity and its restoration through the use of new green technologies and eco-innovations man can at least partially repair what he destroyed in the past. Man should protect the biosphere and climate, should restore the biodiversity of natural ecosystems with a view to the future of future generations of people, the future of the planet, the achievements of the evolution of life on planet Earth, and so on. If man in his nature is friendly towards the biosphere and not selfish towards the planet, the only planet he has, then he probably wants to save the climate, biosphere and biodiversity from total degradation. Accordingly, in recent years there has been a growing demand for the creation and implementation of new green technologies and eco-innovations. New research and implementation centers and new research projects are being established to develop new technological solutions so that the process of green transformation can be carried out more efficiently and quickly. And time is of the essence, as the process of global warming continues to accelerate and there is little time left to reach a critically high state of greenhouse gases in the atmosphere. Besides, thanks to the developing cooperation between scientists and researchers studying this issue, working in different parts of the world, the chances of realizing the plan to save the climate, biosphere and biodiversity from total degradation are becoming greater.
In view of the above, I address the following question to the esteemed community of scientists and researchers:
With the smooth green transformation of the economy, building a green, sustainable, zero-carbon closed-loop economy, and with the large-scale implementation of new green technologies and eco-innovations of zero-carbon energy, etc., will it be possible in the future to restore the biodiversity of natural ecosystems previously destroyed by man, the loss of biodiversity of natural ecosystems made by the development of civilization?
Will it be possible to restore the biodiversity of natural ecosystems previously destroyed by man, made by the development of civilization loss of biodiversity of natural ecosystems, thanks to new technologies?
And what is your opinion on this topic?
What is your opinion on this issue?
Please answer,
I invite everyone to join the discussion,
Thank you very much,
Warm regards,
Dariusz Prokopowicz
The above text is entirely my own work written by me based on my research.
Copyright by Dariusz Prokopowicz
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Not possible in all ecosystems. Possible in some occasions only and it takes a prolonged time. Because natural ecosystem was not established in a single year or even decade. Using modern technologies we protect the ecosystem from anthropogenic activities and nature will heal the wounds slowly; we will encourage it.
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In the advent of climate change, conditions suitable for local species could be significantly altered. Hence, planting characteristic tree species of the planting sites may not be feasible. There are several pieces of literature recommending the use of composite provenance in order to restore climate-resilient characteristic tree species/forests. However, the issue of outbreeding depression is a concern. So, my question is: in the advent of climate change, would it be wise to use planting material from composite provenance for forest restoration?
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with respect to everyone’s comments; we’re long past the relevancy of researching local or non-local sourcing. As late as the 1960 we’ve been researching and implementing restoration ideas applied to forests, wet lands, underwater coral forests and arid land. Done so with a equal number of academic discussion on which approach is best. But…climate change is increasing rapidly. We’ll soon be forced to apply whatever we can to a wider array of areas and hope that the destructive force of increasingly severe storms doesn’t wipe away our efforts. We’ll need to accept composite provenancing approach may risk introducing some maladapted biology………….We don’t need funding for one more study. ……..We need people applying this now. Particularly in countries already experiencing changes to their environment.
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Progressive climate change, including the process of global warming, is causing increasing droughts and desertification of areas. The scale of areas with decreasing rainfall is growing. Surface and sub-surface water resources are decreasing. Water resources for irrigation of agricultural fields are decreasing. Drinking water supplies are also declining.
In view of the above, the question becomes increasingly topical:
What are effective solutions for saving and recovering potable water?
How can field irrigation systems be developed in a situation of water scarcity and increasingly frequent periods of drought?
How can water scarcity problems be solved?
What do you think about this topic?
What is your opinion on this subject?
Please reply,
I invite you all to discuss,
Thank you very much,
Regards,
Dariusz
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Your question is worded very confusingly. Let's break it down into parts, if you don't mind. Despite global warming, the total amount of water in the hydrosphere and atmosphere does not change. I think there is no doubt. During global cooling it is different. During global cooling, the total volume of water in the form of gas and liquid decreases, this water is stored above the ocean surface in glaciers. The ocean level is dropping. Everyone knows this. During global warming, evaporation from the surface of the earth and water increases and water from the hydrosphere passes into the atmosphere. The rain is getting bigger. I think there is no doubt. It rains more and more people die because of the drought. This is true and it is a paradox. If there is interest in this issue, I will continue.
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what is the general trend in the R:S ratio of tree species at the seedling stage? early-successional vs. late-successional which ones have big R:S ratio? i see some contradicting results published. Plus, could these trend vary with tropical and temperate tree species?
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May be 3:1
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Has anyone been able to successfully cryopreserve coral oocytes? I've only found one case for a Gorgonian (Junceella juncea) through vitrification (Tsai et al. 2015, attached below). I know that in some cases some researchers (personal communications) have been able to thaw and retrieve from liquid nitrogen, but though they are still 'alive', they loose their ability to be fertilized (infertile).
I appreciate your help providing me with your answers and/or experience in this matter.
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Everything is very simple. They are prepared in the same way as mammalian eggs. Deep freezing takes place in liquid nitrogen. There is also an article, unfortunately in Russian.
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25 years ago while replanting a 100-mile gas pipeline north of Reno in BLM lands in a cheatgrass area, at http://www.ecoseeds.com/greatbasin.html discovered that the exotic animal grazing had lowered the soil nutrients and organic matter below the thresholds needed for the local native seedling survival, that you can see at http://www.ecoseeds.com/good.example.html
By finding the soil nutrient thresholds in the top 5 cm, from around the seedlings of the desired native, and then testing the project area soils, and then adding fertilizers and organic matter along with the seeds, was able to get a cheatgrass-free planting in only six months, that remained 100% cheatgrass free for at least five years.
So my conclusion is that cheatgrass, instead of an "invasive" plants, the cheatgrass is what I call a "default" weed, only growing in soil too poor for the local natives and indicating poor soil conditions.
THE QUESTION IS, has anyone else used fertilizers to permanently eradicate other populations of cheatgrass, or added fertilizers to bring the soil nutrient thresholds up, so that the desirable plants are favored, and they can out-compete with the poorer-soil adapted weeds?
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Collaborations may be forthcoming if I can find anyone working on plant assisted colonization.  It can be anywhere in the world and any habitat.  I want to try out a decision framework recently published on AC and the biogeographic approach.
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I have established an experiment on A. nebrodensis, a Sicilian fir growing on the Sicily mountains. The whole remnant gene pool has been grafted and transferred toward a northern Apennine site. Each step is monitored, who will come after me will continue that....
Konnert, M., Fady, B., Gömöry, D., A’Hara, S., Wolter, F., Ducci, F., Koskela, J., Bozzano, M., Maaten, T. and Kowalczyk, J. European Forest Genetic Resources Programme (EUFORGEN). 2015. Use and transfer of forest reproductive material in Europe in the context of climate change. European Forest Genetic Resources Programme (EUFORGEN), Bioversity International, Rome, Italy(E ISBN 978-92-5-107538-8): xvi and 75 p.
Ducci F., 2014. Species restoration approach 15.1. Species restoration through dynamic ex situ conservation: Abies nebrodensis as a model. In: Bozzano, M., Jalonen, R., Thomas, E., Boshier, D., Gallo, L., Cavers, S., Bordács, S., Smith, P. & Loo, J., eds. . Genetic considerations in ecosystem restoration using native tree species. State of the World’s Forest Genetic Resources – Thematic Study. Rome, FAO and Bioversity International. ISBN 978-92-5-108469-4 (print), E-ISBN 978-92-5-108470-0 (PDF), © FAO, 2014: 225 – 232.
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I just published a satirical article in a serious journal, and it has a serious argument. The intent was to use satire as a transparent tool to show the limitations of current methods, and to potentially launch more radical ideas that would be capable of more beneficial outcomes.
But there are a lot of problems with satire: it's frequently misunderstood, authorial intent looms inappropriately large, and perhaps it wouldn't be taken seriously. After the scandals around the Sokol paper, and the more recent expose in the humanities, do you have any opinion about when satire would be helpful and when not? Thanks for any thoughts :)
Brick, C. (2019). A modest proposal for restoration ecology. Restoration Ecology, 27, 3. 10.1111/rec.12943
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If we limit "intellectual discussion" to research articles published in peer-review high-quality journals, I would say that satire is an attempt to redefine the genre of the research article. Regardless of its intentions, challenging a well-established conventional genre may take time, and may only stand a chance if authors, readers, the community of practice and the gatekeepers see value in it.
It may be helpful to think of a satirical research article (serious journal, serious argument) in terms of the notion of small "c" creativity (Sawyer) and the propulsion theory of creative contributions (Sternberg) -- see http://www.robertjsternberg.com/investment-theory-of-creativity.
Using satire to make a serious point is something that's creative insofar as it may have some originality (this is purely a frequency statement -- you don't see satire a lot in a research journal) but whether it's also meaningful is questionable.
The Sokol affair (strictly speaking the article was a parody) shows that humour has not really caught on as an acceptable way for communicating research findings, with or without an element of social criticism or critical reflexivity; we're nearly 25 years on and similar cases are far and few between.
If there was a larger proportion of these articles across a wide range of disciplines and journals, it could be seen as a form of redefinition or reconceptualisation but that's not yet the case. This would mean that satirical research publications are in fact a form of regressive redirection, a return to some idea, something new that has, however, been discarded before.
As you point out, there are a lot of problems with satire and other forms of humour. When combined with the time it takes to write a satirical piece and getting it past the editor's desk and peer-reviewed, I would say the benefits are not worth the potential risks and harm.
In fact, what is beneficial -- and is a well accepted practice across time and space -- is to introduce sincere intellectual discussion into satire and other genres and forms of literature and art. This may point to a certain cognitive bias.
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To assist in weed management objectives, I am seeking information on tropical grass re-establishment methodologies and key references that may help a conservation area in Java, Indonesia.
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The indigenous grasses of Eastern Africa have been exported to Australia. Especially the c.ciliaris( fox taii) and guinea grass (panicum). The Tropical Savannah Project of Australia should give best advice as Java is close ecologicaly to Australia.
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What is meant by ecosystem health?
Give an idea of ecosystem health profile.
State the indicators of ecosystem health?
How health deterioration is diagnosed?
How can health of an ecosystem be recovered?
What protective and ameliorative or therapeutic strategies can be adopted?
How indicators can tell about the good health, the bad health, deteriorating health or the recovering health?
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Hi Jayanata,
In his seminal 2003 book entitled "Managing for Healthy Ecosystems" (CRC Press) David J. Rapport refers to ecosystem health as the "capacity of a system to perform normal functions." In the Preface to the book the authors suggest that  "Ecosystem health  embodies the capacity of ecosystems to function without impairment." If you can get a copy of this book it is well worth it. To give you some idea how the concept of ecosystem health is being used in marine sciences I have attached a few reviews that you may find interesting. I hope this helps a bit.
Tomas
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Here in Lithuania we face a contrary issue - how to reduce Phragmites australis populations which overgrow some medicinal plants and other wild harvested species. They occupy every more or less suitable site including quite dry habitats. This case looks like a population shift to the North, which is predicted by the climate change researchers. What about the other wetland plants in Central Italy - are there any more species who suffer regression too? E-mail: juozas.labokas@botanika.lt
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Dear Juozas, I'm from Central Italy and I studied with my colleagues the problem. My answer to your question is: I believe in Lithuania the fast spreading of P. australis could be definitely dependent by climate changes, however in Central Italy the problem is probably much more complicated. P. australis is a species with very wide ecology. It can grow in regions with subtropical to temperate climate; in acidic to basic soils temporary to permanently flooded; in olygotrophic to eutrophic and fresh to brackish water. Central Italy is in the middle of the distribution area, not at the edges, so I don't think climatic change can affect directly so much the populations. What instead is true is that climate change is an important factor that affects the seasonal speed of drying out and eutrophication of water bodies. Now the hypothesis for the dying back also reported in the literature are really many. According to my experience in Italy and in other countries my personal main observation is that P. australis population can start to dye for many different localized reasons (rapid decreasing and increasing of water level, chemical pollution, vegetation succession, etc...), from this point what usually happen is a negative feedback mechanism. more and more plants dye, more organic matter deposits on the bottom, less oxygen is in the soil, lower is the regeneration of the the plants, more pathogens attack the plants and so on... up to the compete disappearance of the population. 
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I'm looking for literature on tropical dry forest restoration worldwide. If you know of any projects, I would be very grateful if you could let me know about them. Thank you all
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I found this to be quite informative.
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I have an experimental set up where I look at oak regeneration. I have taken hemispherical photographs in order to estimate the percent of above canopy light that is available to the seedlings under different canopy conditions. My supervisor have done this before, but analyzed the images using Gap Light Analyzer. Now that software is to old to run on my computer, so I am wondering if anyone have experience using the software CAN-EYE to answer similar questions? I have spent hours reading their manual, but since I'm new at this I still can't figure out if it can do what I want...
Thank you!
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Madam Linda, I have a simple answer to your question.  However, you need a computer programmer to devise a code to count the number of pixels in an image.  Take some JPEG photos in the canopy, then using a software called IrfanView, you can convert the pictures into monochrome and this is where the programmer will devise a program that can count the black and white pixels.  The white pixels represent light that is penetrating the canopy.  
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Bonjour,
wanting to study bryophyte seed banks in temperate temporary wet ecosystems (ponds puddles etc.) I am looking for any practical advices and/or relevant references. Thank you.
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Thank you all for your answers
"seed bank" is indeed a common locution to refer to the diaspores (seeds, spores, fruits, propagules, etc.) which can be found in a soil. As for Bryophytes of course this is limited to spores and propagules.
Bonjour
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Both phytoextraction efficiency (PEE) and metal accumulation index (MAI) are key parameters to know the ability of a plant for heavy metals removal from a contaminated soil. Are there any other indices?
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Dear Anand, For determination of phytoremediation potential I used Translocation Index, Bioconcentration factor (BCF) and Extraction coefficient.  С,% = СHM in vegetation (mg/kg) / СHM in soil (mg/kg)*100% С -Extraction coefficient.
I hope this help. best regards Asil Nurzhanova 
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In restoring ecosystem, nurse plant can be used to facilitate other plants establishment so that successional process can run faster. What I am wondering is, when I need to decide what kind of plant that I should grow under nurse plant, I don't know which one is better, pick shrubs/grass or tree seedlings? I have heard that tree seedling is better because it can cut some successional steps. In the other hand, facilitating shrubs/grass may develop soil so tree will be able to grow in that soil condition.
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I forgot to mention, we tend to sow grass at first time or season possible for growth and trees are planted during dormant season before growth season begins.  In droughty areas, if we do any ripping of soils on the contour, we would plant the trees in the rips and tamp them in good, as they depressions are likely to capture some excess rainfall or surface water.  In consistency wet areas with high water tables, planting trees on the higher areas when possible is going to be beneficial.  Only certain species can handle the driest and wettest areas, so pick them to fit the circumstances.  If soils are mapped or you have questions, discuss with soil scientist, forester and botanist or ecologist.
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In the field restoration and reforestation
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Hi Mohandass,
Here are some useful pdf attachments for your persual.
Good Luck
Dr. Arvind Singh
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I´m looking for different ways to find relationships between litter production and the ecosystem services in a process of restoration ecology and know how can I size and quantify it.
Thank you very much, any help will be welcome.
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Hi there,
From the point of view of coastal ecology, litter production is important for ecosystem services. Litter, produced in mangroves and saltmarsh, supports nearshore fisheries. An early review examined the outwelling of mangrove litter. Please refer to the reference as below.
In addition, litter production contributes to sediment carbon accumulation in coastal ecosystems. Please also refer to my review paper re sediment carbon burial of saltmarsh.
Hope it helps.
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in most articles i get adding 50g of arbuscular mycorrhiza inoculation(sand,soil,host root) is sufficient to do AMF inoculation research. is that always true? deos it hold true if i want to inoculate a tree seedling(potted in a 15 cm plastic pot) during planting on the field?
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you can use 3000 AMF spore innoculant per square metre...
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Brush fire usually happened in somewhere during the hottest Summer of Australia.After put out the fire, is there any methods which linked with landscape architecture can used to help the vegetation restoration of the area? Thank you.
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Let me ride on the responses of collegues above. In such case indigenous plants which are known to be tolerant can be used. In some regions such as the Sahel, farmers are aware of plants that can re sprout after fire or damage. These can be used depending on the ecosystem and it's variability. 
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I intend to gather information about the plants which existed before the KGFs were mined systematically. 
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Please go through the following literature to know the answer
S. R. Ramesh (1990). Studies on the Flora of Kolar District, Ph.D. thesis, University of Mysore, Mysore.
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founders effect is usually referred as loss of genetic diversity due to small population size of pioneers. however, i also rarely read that founders effect denotes to the effect of early colonizing or planted plants on the over all succession and hence, restoration success/speed of a restoration site. so can some one tell me a little bit on this matter?
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I do agree with Truman that the expression in Lamb and Gilmour is a generalization at community level, which includes priority effects. However, founders effect is a population level phenomenon. Strictly speaking, it should be looked at individual species population level.
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What are the top research needs to advance the field or to make projects more effective?
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Dear Kate,
One of the biggest gaps is still the evaluation of the restoration success. My field of research is freshwater ecology (so, river restoration in this context) and the problem is as follows: The EU-WFD has led to great efforts in river restoration so that "all surface water bodies will reach a good ecological state by 2015" (or 2027 for many). Billions of Euros were spent on restoring river stretches, but in only a few cases a proper monitoring was conducted afterwards. This is because of a lack of funding for such long-term research activities (revisiting a restored site 1, 5 and/or 10 years later) and so we effectively still do not know if all that money spent will result in a "good ecological state". Recent studies have shown that in many cases river restoration measures did NOT lead to an improvement of the ecological state (measured as a multimetric index using the macrozoobenthos, the fish fauna, macrophytes and the phytobenthos). It has been argued that the time between the restoration and the evaluation was too short for showing any improvements, but my own research (Groll 2011, submitted) and studies analyzed by Haase et al. (2015) show that even 10 or 20 years after the implementation of a restoration measure hardly any effect can be measured. One possible explanation could be that we just measure the wrong things (e.g. that the metrics used for the assessment are not matching the natural succession in certain river types) or that other, more indirect parameters (especially the land use in the upper catchment) have a paramount influence on the ecological quality and thus superimpeed any restoration improvements.
In essence the water administrations, who initiate and govern the river restoration efforts are still in the dark about if the money is spent wisely or not (and cost-effectiveness is one main aspect of the EU-WFD).
My argument is that we still need to know more about the detailed relations between the species used for the assessment (e.g. the macrozoobenthos) and their habitats (as the riverbed features that can be affected by a restoration). The classical "build-it and they will come" paradigm clearly doesn't work and needs to be replaced by a more in-depth and probably more holistic assessment of the conditions of and the changes in restoration sites, as these knowledge gaps can only be closed by gathering more data (both before and after) of successful and unsuccessful restoration measures.
***
Bernhardt ES, Palmer MA, Allan JD, Alexander G, Barnas K, Brooks S, Carr J, Clayton S, Dahm C, Follstad-Shah J, Galat D, Gloss S, Goodwin P, Hart D, Hassett B, Jenkinson R, Katz S, Kondolf GM, Lake PS, Lave R, Meyer JL, O’Donnell TK, Pagano L, Powell B, Sudduth E (2005) Synthesizing U.S. River Restoration Efforts. Science 308: 636-637
Dickhaut W (2005) Fließgewässerrenaturierung Heute – Forschung zu Effizienz und Umsetzungspraxis – Abschlussbericht.
England J, Skinner KS, Carter MG (2008) Monitoring, river restoration and the Water Framework Directive. Water and Environment Journal 22: 227-234. doi:10.1111/j.1747-6593.2007.00090.x
Giller PS (2005) River restoration: seeking ecological standards. Editor's introduction. Journal of Applied Ecology 42: 201-207. doi:10.1111/j.1365-2664.2005.01020.x
Groll M (2011) Beziehungen zwischen der Gewässermorphologie und dem Makrozoobenthos an renaturierten Abschnitten der Lahn. Dissertation am Fachbereich Geographie der Philipps-Universität Marburg.
Groll, M (submitted) Is the self-reinforced river restoration approach an efficient tool to achieve the good ecological status? Morphologic and faunistic results from two restoration projects in the German lower mountain range. Environmental Earth Sciences Thematic Issue – Water Resources and Research in Germany.
Haase P, Birzle-Harder B, Deffner J, Hering D, Januschke K, Kaffenberger N, Leps M, Lorenz A, Modrak P, Stoll S, Sundermann A (2015) Ein neuer Blick auf die Fließgewässer-Renaturierungen – Wirkung auf Fluss, Aue und Mensch. Endbericht der Senckenberg Gesellschaft für Naturforschung: 74 p
Koenzen U (2008) Erfolgskontrolle von Maßnahmen zur naturnahen Entwicklung von Fließgewässern – Hinweise für gezielte Maßnahmen zur Kompensation von Strukturdefiziten unter Berücksichtigung der Strahlwirkung. In: Deutscher Rat für Landespflege (eds) Kompensation von Strukturdefiziten in Fließgewässern durch Strahlwirkung, Schriftenreihe des DRL 81: 35-42
Moerke AH, Lamberti GA (2004) Restoring Stream Ecosystems: lessons from a Midwestern State. Restoration Ecology 12 (3): 327-334
Newson MD, Large ARG (2006) ‘Natural’ rivers, ‘hydromorphological quality’ and river restoration: a challenging new agenda for applied fluvial geomorphology. Earth Surf. Process. Landforms 31: 1606-1624. doi:10.1002/esp.1430
***
I hope that helps.
All the best,
Michael
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We're studying the feasibility of restoring aquatic habitat to a 1.2 km (4,000 ft) length of river pool on the Upper Ohio River. Restoration may include adding large river substrate, terracing the river bank, adding perched wetlands, etc.  We were wondering if there exists any habitat evaluation model/procedure that would allow us to assess potential benefits holistically, i.e., in a linked, perhaps synergistic fashion.  Our evaluation alternatives, at this point, are to use something like time-worn HSI models (e.g., for Smallmouth Bass).
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I might go off on a tangent here, but from my experience (or better: from German/European experiences from the last 30+ years) I would say that things linke adding large substrate and terracing the banks are neither necessary nor advisable. They are usually quite expensive and after a larger flood event or two none of it will remain (or it has to be maintained which costs even more money). In Germany the authorities now like to apply an approach that allows for a self-reinforced development of the river morphology. This include removing the bank fixation and often (where necessary) the removal of parts of the topsoil (in order to decrease the height difference between the water level and the floodplain). In many cases large woody debris (or boulders)  is also fixated in the riverbed in order to guide the current and promote bank erosion. These combined measures usually do not cost more than 150€/m, while more traditional restoration measures (riverbed modelling, planting of riparian trees, 5-years maintenance and so on) add up to usually up to 2000€/m.
My PhD focused on the evaluation of two such self-reinforced restoration measures with a special focus on the riverbed morhphology and the macrozoobenthos and the results show that these simple measures are very effective in enabling a more natural substrate and habitat dynamic, especially if flood event speed up the process.
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I conducted a study on our university's freshwater lake located in our nature preserve. Now, we are in the process of restoring it.
Can anyone recommend any important plants/trees needed to suck up nutrients and filter the water?
The water is very turbid (visibility is low at about 1-2 ft). P is limiting but about 0.04-0.06 mg/L and N is 1.02-1.40 mg/L, dominant aquatic plant spp is FW macroalgae Chara spp., and it is surrounded by Ardesia and Brazilian Pepper. There is a healthy population of eastern mosquitofish and large mouth bass, but there is a high amount of striped tilapia and african jewelfish.
Average depth is about 6 ft, max depth 9 ft. 
Let me know if you need anymore information.
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1.) BIVALVES--I did not see any mention about any of the 50 species of fresh water Florida native clams or fresh water mussels?  They are good filter-feeders.
2.) WHERE IS TURBID WATER COMING FROM?--No mention why the pond is so turbid-- is turbid water coming into the pond, if so, why not produce a kind of native Florida vegetation filter lining the stream into the pond with some native sedges or wiregrass?  It sounds like this pond is being fed by agriculture, road or lawn runoff? You will probably solve 90% of the pond problems when you fix the source of the turbid water going into the pond.
3.) POND EDGES--And what about the pond edges, solid native plants along all of the edges, or are there bare areas?  Three feet above and one foot below the water line should be covered with native vegetation
4.) EXOTIC PLANTS OUT--And chop down all of those exotic Ardesia ( if they are either crenata or elliptica) and the Brazilian peppers if you can, because their leaves dropping into the pond could be having an effect.  However if you have Ardisia escallonioides, that is a Florida native, so keep that.
5.) EXOTIC FISH OUT--And what about fishing out the exotic fish?  Mmmmm, fried tilapia barbeque?
Also, you did not mention the size of this pond? 
Basically you will known that you fixed your pond, when you can see to the bottom.   Keep experimenting and get a Secchi disk and measure the turbidity at least twice a month, to see how well you are doing on the turbidity.
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How can we quantify ecosystems health? What are the criteria to be consider for us to say that a certain ecosystem is healthy?
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Personally I would avoid using the term "ecosystem health".  It's one of those phrases that is used without any real thought as to what it means, and once you start pulling it apart means nothing at all.  Any ecosystem that supports its component species could be considered "healthy". but that would include ecosystems that appear very degraded from a human perspective, e.g. a highly eutrophic lake.  It's much better to think in terms of ecosystem functions, flows of energy and nutrients, presence of native species and their interactions, etc.  
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I would like to access some of the plant traits information in this site (seed mass, heigth and so on), but I don't know if I have to ask for it in every case. Some previous experience with this site that can help me? Thank you.
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Thanks! I did indeed solved this. luckily in Germany there are other very good databases, so I settle with that. 
Regards, 
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Can some one send me a practical positive result(s) in ecological restoration that is (are) obtained from the application of AMF. i read some article regarding some good experience in Spain (Barea et al). are there more of such examples? is the role of AMF in ecological restoration a practical one or its just a myth? many thanks in advance.
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The most visible effect of AMF was observed in Coffee, even in areas where the soil is deficit in P and other key nutrients. Enjoy the attached review, though few years old.
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Does anyone know where I can find information/data documenting the loss of native Floridian ecosystems, including mangrove islands, wetlands (marshes and swamps), pine flatwoods (both long leaf pine with wire grass and slash pine with palmetto), temperate hardwood forest and mesic hammocks.  thanks!  
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There are a variety of sources at different scales geographically with varying accuracy to answer your question. If you want statewide estimates I recommend Myers an Ewel Ecosystems of Florida. I have work on this for the Charlotte Harbor portion of southwest Florida. The ecosystems section of the South Florida Multi-Species Recovery Plan is a good location for information for the area south and flanking lake Okeechobee inlcuding the Everglades, Big Cypress and the Keys  See http://www.fws.gov/verobeach/ListedSpeciesMSRP.html .
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Based on Lewis (1990), 3 terms for Restoration named, "restoration”, “creation”, and “enhancement” have been defined. Also Restoration can be divided in two parts as “Rehabilitation” and “Reestablishment”. There is no name for "Revitalization" here.  My dissertation is about Revitalizing urban wetland's cultural landscape. Though I couldn't find any classification –method or any common way-  for wetland's Revitalization. Now, my question is:
Could Restoration and Revitalization be the same? Can I use revitalization term instead of restoration? If not, what are the differences?
Could you please introduce me any professor or expert in this field?
Thank you in advanced for your answers and attentions.
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Dear Negar,
I am not a wetland scientist, but I am an applied limnologist, or "lake manager".
I have never heard the term "revitalization", but maybe the following may help you.
Two terms are used in modern lake management: (lake) restoration and (lake) rehabilitation.  The introduction of the term "rehabilitation" is more modern, and you can find the original definition and rationale in Cooke (1999).  As far as I know, the definition still stands today.
The matter is concisely reprised in Cooke et al. (2005: 14), and I reprint the original statements verbatim (but abridged) from here:
"In the strict sense, restoration means returning something to its original form.  With the possible exception of dredging, which removes nutrients, excessive vegetation, and sediment, hopefully toward a former state, other lake treatments are not true restoration activities.  Restoration (sensu strictu) is defined (Webster 1972) as "the bringing back to a former or normal condition, as by repairing, rebuilding, and/or altering."  Cairns et al. (1992) defined restoration as "the return of an ecosystem to a close approximation of its condition prior to disturbance."  They recognized that actual restoration is not possible.  The pre-disturbance species list and the chemical, biological, and physical interactions for a lake and its watershed are not known for any lake.
A more accurate term for what we, as restoration ecologists, are attempting, is rehabilitation (Cooke 1999).  Rehabilitation means re-establishment of important missing or altered processes, habitats, concentrations, and species [...]  This concept emphasizes return of degraded systems to attainable approximations of pre-disturbance conditions, and the establishment of protections against future disturbances."
So, rehabilitation is restoring a lake (or any other ecosystem) to a condition that is functionally very similar to the pre-disturbance condition, but the lake ecosystem will not be exactly as before (e.g., different biological species composition).
Based on your question, I would then say that "revitalization" is closest in meaning to "rehabilitation", but then again I'm not a wetland scientist.
I do not know if Cooke et al. (2005) is easily available in your country.  You can order it online at the publisher Webpage at the link provided below.  As far as I know, there is no plan for a fourth edition of this book.  (Dennis Cooke, the first author, has been my academic advisor in my graduate studies, so I can enjoy first-hand accounts in this regard.  Dr. Cooke is an Emeritus Professor and has since retired from active research, but I'm quite positive that the info that I provide here is pretty much what he would tell you directly.)
I hope that this helps a bit.
Best of luck with your Thesis!
-Paola
Cairns J. et al., 1992.  Restoration of Aquatic Ecosystems -- Science, Technology, and Public Policy.  National Academy Press, Washington, DC.
Cooke G.D., 1999.  Ecosystem rehabilitation.  Lake and Reservoir Management 15: 1-4.
Cooke G.D., E.B. Welch, S.A Peterson & S.A. Nichols, 2005.  Restoration and Management of Lakes and Reservoirs, 3rd edition.  CRC / Taylor & Francis, Boca Raton, FL.
Webster, 1972.  New World Dictionary.  World Publishing Co., New York, NY.
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In a new version (Canoco 5) there are few new options: variation partitioning build - in the analysis, use of GLM, and the possibility to use traits data. Does anybody have experience with Canoco 5 already?
1. Particularly in analyzing change over time in the plant community (with a additional factor acting at the known moment in time, but not incorporated in the environmental data sensu stricto). I know the principal response curves procedure, I'm wondering if there is a different/better approach.
2. Analyzing the changes of mean plant traits over time in community, but within a relatively small data set (something like 16 plots, recorded for a couple of years). Is this even possible? what kind of results do you get? What are the possible mistakes in interpretation?
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You get some guide book to read before you take analysis. Book: multivariate analysis of ecological data using Canoco. If you need it I can share to you
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I am trying to quantify the time needed for indirect canopy regeneration of burnt areas (i.e. from patches or individuals that didn't burn). Did somebody com across any estimates of primary and secondary dispersion of seeds? Also what factors could prevent this process?
**Edit***
As suggested by S. Hari I specify that I am interested in particular in mediterranean low forest, composed both by pioneer (seeder) and postpioneer plants and where crown fire are the most common. My question arises from the need to give indication to forest workers on when they should look for signs of recovery
Thanks
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It really depends on your ecosystem and species involved, as S. Hari indicates.  In many places the pulse of recruitment can last decades, with gradual infilling; in others, if recruitment doesn't happen right away, grasses, sedges, and other species can out compete seedlings for water and succession much delayed.  There are many things that influence this rate- climate in the following years, distance from the intact edge, whether it's a good seed crop year for the survivors, herbivory/seed predation, etc.  Also the intensity of the fire may matter, if it alters the biogeochemistry or physical properties of the soil in some way (at least some abnormal way).
So overall, it really depends on the system and species.  In most places, though, you've got to give it a few years for seed from the outside.
I would recommend looking for post-fire studies in your ecosystem and then looking into the methods sections to see how long post-fire the study was done.  But again, other things will matter which vary, like climate, distance from edge, etc...
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Focus on: criteria for selection, establishment, conservation, management and  monitoring
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Dear Louhaichi,
You can surf Journal of Arid Environmental (http://www.journals.elsevier.com/journal-of-arid-environments/). There you'll find papers a lot about conservation in that arid habitats. Good luck.
Best regards.
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Soil bioengineering is the use of living plant materials to perform some engineering function, from simple erosion control with hydroseeding to more complex slope stabilization with willows and other plants (Schiechtl 1980).
Pioneering woody species are of particular importance in the development of bioengineering systems. In Mediterranean countries the water stress resulting from a dry summer is a limiting factor for plant success, and the plant selection for bioengineering should consider the more suitable native species.
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If you are also interested on wetlands restoration you can contact with Maria A. Rodrigo Alacreu, from ICBIBE (University of Valencia): http://www.uv.es/~rodrigoa/
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In California, serpentine soils contain unique native species, and also contain some of best examples of wildflower fields, but when projects like pipelines go through, there do not seem to be any successes in rebuilding those areas from scratch.  
Any successes within California or in serpentine in other parts of the world, and what was the plan? With the lack of restoration knowledge of serpentine in California, I am estimating at least $5 million per acre to invent the methods we need to succeed.
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In Piedmont Pennsylvania, where I'm very much involved in serpentine grassland restoration at several sites, we are achieving good success and learning as we go by applying the adaptive management approach, which includes applying experimental design principles to routine management activities and monitoring carefully selected key indicators long-term. This is evidence-based management in which a management team is accountable for the results. You can see two adaptive management plans for serpentine grassland restoration on my website. Go to www.continentalconservation.us, click on Publications, scroll down to Other Recent Publications, and download the first and fourth items. Implementation is well underway at both of those sites. Incidentally, my ResearchGate profile photo was taken at a serpentine grassland in Riserva Naturale Monterufoli-Caselli, one of several protected areas of serpentine vegetation in Tuscany, where, in the 1580s, Andrea Cesalpino was the first natural historian in the West, and maybe anywhere, to note a connection between plant species distribution and bedrock type.
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On every spot where any individual exotic plant gets established, it is causing what I call "Spatial Extinction" of the local native plants on the spot that the exotic plant is occupying. We usually consider "extinction" is the final death of every last individual of the species, but I am suggesting a new concept, that when an individual exotic plant gets established, that it is causing "Spatial" extinction, that lasts as long on that spot and is as effective as regular extinction is. Pictures from California, Poppies and a few feet away solid European foxtail grass causing Spatial Extinction of the native ecosystem.
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Your concept is flawed, until you take into account the seed banks.  In Mountain Fynbos and some Lowland Fynbos species, seed banks may persist for 3 fire cycles (45-100 years) under 100% cover alien (pine and wattle) stands.   
It stands to reason that "spatial extinction" in these cases only occurs after 3 generations.  If in the meantime a biocontrol is introduced (see the extensive South African literature), or moves in (e.g. Zulubius on Acacia cyclops), or "evolves" (e.g. switching hosts - examples??) within the 3 generations (or land use management changes) then spatial extinction may be forestalled.
Also spatial extinction is likely to be selective: short-rotation species may for instance be able to survive with the alien (completing their life cycle before a longer-lived species can re-establish full closure following a disturbance), whereas long-lived understorey species may be selected against (and canopy-stored seed bank species extremely strongly selected against - extinction occurring with the death of the last individual plant), but of course, it is the seed bank longevity that determines time to extinction.
For your concept to work you need to generalize it to more than systems of annual or near-annual plants with seed longevity of the same order of magnitude.
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NGS platforms, sequencing whole genome of an individual in few hours, are being used in bio medical sciences tremendously and in agricultural and environmental sciences upto a some extent. Soil microbes play key role in degradation of organic matter, biogeochemical cyclying, soil structure formation and ecosystem structural and functional stability. How knowing understanding structure, function and diversity through NGS platforms can contribute in ecosystem restoration process?    
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Dear Craig,
Why don't you perform a research first taking into ocnsideration genetic variability with molecular markers (you can collaborate with people from breeding programs for grasses) and / or biomarkers or barcodes for grasses (reeeeally don't know what information to count on in literature but there's something interesting concerning markers and taxonomy) and, after that you can select the "different" ones to further characterization if need. Could be interesting...
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I like to think of this a tool being used in conjunction with other restoration practices (planting, seeding ect), but not sure what other folks think of it.
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Since you are in California I assume you are talking about grassland habitats?  Or riparian?  If grasslands, there are three basic methods to deal with the weeds, to get back to as close to 100% native cover, that you can see examples at http://www.ecoseeds.com/WMA.html.
1.) Mark Van De Pol 14 acres in the Santa Cruz Mttn. went from 1% native cover to 99.5% by spraying the weed seedlings in winter as they germinated.  That means you need to learn was the seedlings of both the weeds and the native look like.   All of the natives the grew back were dormant seeds in the soil underneath the weeds that sprouted once the weeds were sprayed out.
2.) Michael Shaw's 74 acres south of Santa Cruz, went from 1% native cover to 93% cover, by mowing all of the annual weeds before seeds ripen, and the perennials were cut and wick-applied herbicides of the cut stems.  As with Mark's place, all of the native that sprouted up, were dormant seeds, and you can see the list of weeds and natives at http://www.ecoseeds.com/shawlist.html,
3.) My Arastradero preserve project at http://www.ecoseeds.com/arastradero.html, where I am using both weed straw harvested after the seeds have shed like wild oats and Italian thistle, plus native grass straw, as a 3-4 inch deep mulch to cover all the annual weed patches in summer, to kill the germinating weed seedlings from October to December, and then sow or plant in the natives by raking back the mulch.   Was able to get over 99% weed management within 60 days of application of the mulch.
However, for tough perennial weeds like Harding grass or Rumex, only herbicides of the cut stems will control those species,
 
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For instance, do we aim at the point where it was pristine ( which I don't think is possible) or to a point where there is minimal adverse impact?
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Hi Prishnee, the Society for Ecological Restoration International has a primer about using terminology in restoration ecology, e.g., when to say ecosystem restoration vs. rehabilitation. That might prove useful, especially Section 3 "Attributes of Restored Ecosystems", Section 5 "Reference Ecosystems", and Section 8 "Restoration Planning".  I agree with Matteo that the "pristine state" is a problematic reference point for restoration, but more because it would be hard to define what pristine means! Is that before industrialization, before the most recent round of human disturbance? Does the scenario change if the disturbance was natural? Does the environment you are considering have a long-term history of human manipulation, i.e., for centuries or millenia, so removing that disturbance(s) changes the ecosystem? It might prove prudent to consider multiple restoration points, along a trajectory, to buffer against uncertain future changes in the environment (a la Mori 2011 Journal of Applied Ecology).  Best of luck with the project.
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How landscape connectivity influence anthropogenic pressure in biodiversity rich area?
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In California. let's say that 100 native plant species make up a grassland ecosystem, and you start removing the native species one by one, what I call "spatial extinction".
And then at the same time, start adding exotic plant species one by one until you have 1,000 total, and maybe a few exotic animals with equal biomass to humans of cows and sheep. And these new grazing animals are protected from the native carnivores because you have killed them all, and for these new animals the native grassland is a very yummy thing to eat.
Then at the same time, you remove the native peoples by putting a bounty on them in 1853, the people who were managing the native landscape for the last 15,000 years. So there was an important connection between the native peoples and the landscape that has now been broken.
You can clearly see the biotic connectivity when the species are going in either directions. For example you can see when connections are broken as you remove a species one by one, like unplugging batteries from a circuit. Each species of plant and animal contributes its own energy and support to the system.
However, going in the opposite direction, it is much moire dramatic to see those connections return when you reintroduce a native species that has been spatially extinct, and see how fast the connections return--it looks like adding cells to a wound and watching the wound heal. That is what I have seen at my project in Palo Alto, California that you can see at http://www.ecoseeds.com/arastradero.html.
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I manage two very different forests in Mauritius, which we are restoring and I would be keen to learn other techniques to tackling invasive weeds as well as different approaches. We learn a lot from applying successional theory and also trying different techniques, but I would like to know if anyone has published a handbook that is applicable to oceanic or tropical forest management.
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Thanks Graeme. That is much appreciated. I have also bought Restoring tropical forests: a practical guide by Elliot et al. It is always good to get as much information as possible and ideas about how to improve our cost-effectiveness or what different approaches we could use.
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In Central-European riparian woodlands the North-American Box elder/Ash-leaved Maple (Acer negundo) has established itself as a neophyte. The recently reintroduced European Beaver (Castor fiber) is, despite contrary expectations, neglecting the Acer negundo and no trees have been felled.
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Thank you Martin for the quick response.
After a quick overview I see your assumption confirmed that North-American Beavers are avoiding boxelder as well, like their European counterparts.
It would be interesting why, but this is a different question.
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Many restoration/revegetation/reafforestation projects have goals to improve biodiversity or ecosystem services from a degraded site.
Projects often use monocultures of non-native plants (usually trees) or monocultures of native plants (also tends to be trees). However, at considerable cost, some projects employ a diverse planting approach (a few to many species), trying to match the community that was present initially, with the idea that these diverse plantings give better biodiversity or ecosystem function outcomes.
Apart from the initial differences at planting, I'm interested to get people's thoughts on how good the evidence base is for diverse plantings giving better biodiversity and/or ecosystem function outcomes.
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I would agree with Carlos, it very much depends on what kind of community you´d like to restore and what the environmental frame is. In general when you look at ecosystem services it applies to me that diversity targeted restoration is always more sustainable because stability is increased, complementarity in plant traits is fostered (which has positive effect on multiple ES) and cascading effects (sometimes even self-energizing) are likly to be entailed.
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Does anybody know of a good (specific) example where a rehabilitation project for marginal/degraded land resulted in a significant increase in biodiversity, i.e. that the land is now acting as an important refuge for native plants and animals?
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Dear John,
We have published a newsletter about this botanic gardens but its in Arabic. A short article about the gardens and the plants preserved there was published in a publication produced by the UNDP its called Community Action to Achieve Environmental Sustainability (The experience of the Global Environment Facility's Smal Grants Programme in Egypt and the Occupied Palestenian Territory 2013. pp 22-25. hope this is helpfull for you
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I would like to test how dissimilar are some traits of an intruduced species with respect to an established community.
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Hi Florencia,
R packages are the best tool to deal with FD. try downloading the FD package (that includes the vegan package) and you will find a lot of tools in there. you can also choose the dist function or, if you have also categorical variables the gowdis.
Let me suggest you to use more than two traits as some could be very easy to find or measure yourself. the traits you use really depend on what your hypothesis is and you will get different distances of FD indices by using different traits. Some traits could be:
max height, seed mass, wood density (but I'm guessing you are not working with trees),
max photosynthesis, specific leaf area, nitrogen per mass (for these last three you might want to check this article "The worlwide leaf economics spectrum".
The FD package also tolerates missing values, but sometimes you can fill the missing values. for example you could fill them using the value of phylogenetically near species living in the same environment.
Good luck
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I'm looking for a Ph.D. and I would like to know what are the European most active Research Centers in the fields of Landscape Ecology and Ecosystem Conservation/Restoration.
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It's good to be in a happening place, but for a PhD, your advisor is at least as important as the department. I would suggest searching on European landscape ecologists who are doing excellent work. For example, have a look at European members of the editorial and advisory boards for Landscape Ecology (http://www.springer.com/life+sciences/ecology/journal/10980?detailsPage=editorialBoard).
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For instance, for plants we could observe community succession to predict the direction of degraded grassland, for belowground soil the microbes used to be a prerequisite e.g. microbial biomass of carbon and nitrogen. When we obtain data from both community succession and microbes, we usually do some regression and explain the reason for degradation. Could we use other methods?
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The first grassland ecologist 100 years ago in the USA, Arthur Sampson, used particular grassland species to predict trends for either improvements or degradation in grasslands. In California I use percentage native plant cover, zero exotic plants, a low level of bare soil present, and species diversity, and about a 50:50 mix of wildflowers and grasses. If you look at the http://www.confluence.org pictures across the world, you see how rare the non-grass members of the grassland communities are becoming, planet-wide.
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Ronaldo (CR7) just came to my country over the weekend to campaign and support efforts to educate and raise public awareness of the importance of protecting mangrove forests. Is it an effective way?
As we know that over half the worlds mangrove forests have been destroyed over the last 30- 40 years to make way for commercial enterprises such as aquaculture (mainly shrimp farming), agriculture and coastal development. Intensive shrimp farming has devastating environmental effects. Not only does the practice clear large areas of coastal habitat including mangrove forests but it also pollutes nearby coastal waters and marine habitats such as coral reefs with waste matter from the shrimp ponds.
Increased human settlement along our coastlines also leads to agricultural expansion. This is believed to be the most destructive human impact on mangrove forests due to the scale of the problem. Unregulated urban development increases pollution and alters the distribution and use of water and with increased tourism into tropical regions over recent decades; this is only compounding the problem.
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Help people to know more about mangroves is a good way to start:
Then, get people, community and government to preserve, conserve and even replanting mangroves!
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Ecological Engineering is a new baby of Ecosystem Ecology, its principles and their applications are not very different from conceptual ideas and practical applications of Restoration Ecology. However, it is very true that, once severely degraded ecosystem, can not be replaced, or can not be converted in ditto as of the original state.
We can replace or convert a degraded ecosystem into a full functional or up to in–full productive form, but can not be possible to achieve its original shape as it was. Therefore, spirit of my question has posed me to know any possibility for recovering severely degraded or unproductive ecosystem via ECOLOGICAL ENGINEERING discipline whose time has come!!
Based on literature, about 50 % of the total geographical areas of the earth is existing in several format of degradation (anthropogenic, as well as natural calamities). For example India is one of those countries, having a significant size of unproductive/ degraded lands. Moreover, natural calamities like flooding, tsunami and huge human population are also challenging.
If concepts, ideas and practical applications of Ecological Engineering being true, we can reshape and redesign our natural unproductive/degraded ecosystems into most desirable ones.
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Hi Anand,
The short answer is yes, it is possible to restore wasteland areas to ones that are more productive and /or biologically diverse. The amount of resources needed to succeed in the restoration efforts can sometimes be prohibitive though, and continuous running costs can be very high. For example, maintaining irrigation supply to arid areas where crops have been planted. A good article on the limits and goals of restoration ecology is:
Joan G. Ehrenfeld. 2000. Defining the Limits of Restoration: The Need for Realistic Goals. Restoration Ecology Vol. 8 No. 1, pp. 2–9
There are also some very good articles on restoration of wasteland areas in the journal Restoration Ecology. I personally would be more keen on the restoration/redesign of anthropogenically-derived wastelands, rather than tampering with natural desert ecosystems. Desert reclaimation is however, becoming more common in places like China and Egypt. A quick Google search using the term 'desert reclamation' will bring up a lot of information for you.
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We have calculated drift in a 3rd-4th order river in W OR USA, a system that has low nutrient concentrations and perhaps has the capacity to support better anadromous fish runs. We have found limited information in the literature that is comparable to our system and would be interested in hearing from others. We see baseflow as a bottleneck that could be exacerbated by climate change. Part of the problem is methods and how results are reported vary , and there is high temporal and spatial variability naturally.
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Hello: I'm responding because you mentioned temporal and spatial variability. It is pretty standard opinion that plankton abundances (whether marine or in stream drift) are so variable as to be near-chaotic. But the temporal variability should be modelled, i.e. included in the analysis, not treated as noise.
Surprisingly, in data I had for some years, when I began to include the periodic terms to cover the key astronomical cycles (time of day, lunar month, time in year), I found substantial, surprisingly substantial, R-squareds (many in the range of 0.4) in significant regressions. It's documented in this paper: Bell K.N.I. 2007. Opportunities in Stream Drift: Methods, ... Temporal Cycles, In situ Mortality Estimation, and Conservation Implications. In Biology of Hawaiian Streams and Estuaries. Bishop Museum Bulletin in Cultural and Environmental Studies 3: 35–61 (2007). (The paper is downloadable at http://www.ucs.mun.ca/~kbell/pubs/index.html.)
In the paper, p 47, I commented "The results also have implications for how we approach something as simple as comparing two species’ abundances at one site. If we sample, even with replicates, and find that species 2 is twice as abundant as species 1, that simple conclusion could mislead us because the abundance trends of different species can cross each other as the cycle progresses. For example, if we sampled around day 250, we would tend to find many more type W larvae than type F [W and F are operational taxonomic units]; but at day 100 the situation is very much reversed. We must accustom ourselves to think of abundance as not a number, but a pattern...."
You may wish to try it. The methods for periodic regression (and the traps to avoid) are made accessible in my book "Analysing Cycles...". The book is easily available.
Feel free to contact me if you have further questions.
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I'm working on the design of an experiment related to seed bank of road sides, and I'm looking for some alien invasive plant species for it. I already now that Ambrosia artemisiifolia is a major concern in several countries in Europe, but I will need some other species. It would better if they are annuals. Any ideas?
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You could also check the European Alien Species Information Network (http://easin.jrc.ec.europa.eu/). Try the 'combined criteria search' in 'Tools/Services' and select 'Terrestrial' 'Plantae' and 'High Impact'. Apart from the list of high-impact plants (based on DAISIE, NOBANIS, SEBI and CABI) you can also produce distribution maps of one or more species. By pressing the green buttons next to each species you will get relevant information (e.g. links to the factsheets of DAISIS, NOBANIS, CABI.
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Exotic species are better for structural development for soil development at any cost. However, they accumulate substantial amount of biomass but allocation of biomass is somewhat unusual especially in degraded soil. Carbon is one of key element utilized by soil biota for energy and structural development, but carbon accretion in soil by exotic plants is substantially poor (based on my unpublished work).
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Dear Anand Singh,
Recently I was doing some (first literature) study on exotic (shrubs) species and their effects in invaded ecosystems (focused on a one exotic species , originating from N America and behaving invasivally in some sites in Europe). In my opinion its a bit risky business to use the exotic species for restoration (even severely degraded sites). I know it happens e.g. in US, but is rather criticized by restoration ecologists (at the last Ecological Restoration conference by SER Society for Ecological Restoration we had a vivid discussions about it - including so called "novel ecosystem" concept used for it). The arguments are (based on my review): the exotic species usually allocate their biomass above ground - so they can be very competitive & take over more resources (light, nutrients, water). This, usually results in decline of species richness of native species (or simply the native species will not establish). The exotic species may also change characteristics of litter quality (very important!), and because of that affect soil microbial community. Some exotic species were found to have a profound effects on the soil communities (microbial, macrofauna, sometimes promoting invasion / increase of non-native organisms in the soil). They also may have effect on ground-dwelling fauna (eg. result in less species, less individuals or provide food / shelter in the different moments of the cycle than necessary). Change of the litter quality or even some substances accumulated in the soil or roots of exotics can be detrimental for other species - and subsequently lower the prospects of the recovery of an ecosystem ,and establishment of the native species (even some time after exotics are eliminated). This is of course based on studies of other species - but all in all I would say that there is a lot of native species that can be used for a restoration purposes (I am sure there is a lot of species to choose from - India is oneof the ). This is usually a bit more challenging (since many exotic are easy to get in large numbers from the trees nurseries and they are of e.g. a commercial interest - for wood production or so), but in a long run such introduction of exotic may cause a degradation of system (not only in a site itself, but surrounding as well - if it spreads), or simple a situation when much better recovery could have been reached with native species. I agree here with Mr. Karakut that species to be used could be selected in a way , that they are also facilitating growth (establishment) of other species (nursing plants / cover) and pioneer species sometimes make a good nursing plants! Next to planting some of such species it could be considered to: cover the bare soil with some straw / or poor quality hay if available, (mulching) - it usually helps a lot with improving the establishment success of samplings / seedlings. If possible collect some native seeds and spread it there - to accelerated the vegetation establishment (in Europe such method is used with good results I also tested it myself in restoration on degraded peatlands). Please don't hesitate to contact me if you have any questions. best regards dr. Agata Klimkowska, the Netherlands
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Most difficult tasks related to the plant conservation.
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In general - always include society and socio-economics of the region you are working in. It is becoming more and more obvious that "strict" conservation plans which do not take the social level into account will most certainly not work!
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What is the most influential paper in genes-to-ecosystems research that you have read in the past year and why?
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Have run across this paper about four times in several different settings:
Jones, Thomas A. "The Restoration Gene Pool Concept: Beyond the Native Versus Non‐Native Debate." Restoration Ecology 11, no. 3 (2003): 281-290.
Hope all is well with you. Three words: Tree Pose, Raft.
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In arid and semiarid areas?
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The gravel needs to very light weight, full of air bubbles, able to retain water, and preferably light colored. Examples: Vermiculite, pumice. Volcanic cinders worked for the ancient people north east of Flagstaff Arizona, USA for about 200 years until they became clogged with clay minerals.
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Do you know of examples of shortened plant life cycles (like selective hybridization) which have been used to reclaim mine areas and restore virgin forests?
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I've gotten some additional answers back from other restoration researchers. Although not a sterile hybrid, secale spp. have been used to suppress weeds and pave the way.
Herron, G. J., R.L. Sheley, B.D. Maxwell, J.S. Jacobsen. 2001. Influence of nutrient availability on the interaction between spotted knapweed and bluebunch wheatgrass. Restoration Ecology 9:326-331.
Also, from the forestry literature:
Beyers, J. L. 2004. Postfire seeding for erosion control: effectiveness and impacts on native plant communities. Conservation Biology 18:947-956.
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Which groups are doing the work to test, develop and propagate cultivars for this important work?
I know that the NRCS Plant Materials Centers are involved in some of this work. I would like to know the names of other private or government institutions in the US doing this work.
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Thanks Lorinda. I actually just saw the post-doc announcement for MPG Ranch on the ESA job board. In your opinion, how essential is prior experience with molecular genetic techniques when getting into this field? It is certainly something I am interested in and willing to learn--just wondering what angle I would take to get my foot in the door to a position in this field. My experience has largely been field-based plant community ecology.