in this power point i have given the overview of freshwater ecosystem and covered mainly three type of ecosystem i.e lentic ecosystem, lotic ecosystem and wetlands.
in this power point i have given the overview of freshwater ecosystem and covered mainly three type of ecosystem i.e lentic ecosystem, lotic ecosystem and wetlands.
FLORAL DIVERSITY OF MANGROVE ECOSYSTEM FROM COASTAL ENVIRONMENT OF URAN (RAIG...Prabhakar Pawar
Mangrove forests are among the world’s most productive ecosystems and are the only forests situated at the confluence of land and sea in tropical and subtropical latitudes.Mangroves are one of the biologically diverse ecosystems in the world, rich in organic matter and nutrients and support very large biomass of flora and fauna. With continuing degradation and destruction ofmangroves, there is a critical need to understand the biodiversity of the mangrove ecosystems.Mangroves represent spirit of Mumbai and NaviMumbai - they are plucky survivors. Each day, millions of citizens in Mumbai pass these hardy plants imaging they are little more than dirty, muddy weeds growing pointlessly along the shoreline. Overexploitation and unsustainable demand has resulted in considerable degradation of mangrove areas and it is feared that the area under mangroves around Mumbai areas has dwindled by 35% in the last 25 years and only about 20 Km2 of mangroves exist today. During this study, 4 species of true
mangroves representing 3 genera and 3 families, 10 species of mangrove associates belonging to 8 genera and 6 families and 1 species of non-mangrove halophytes were recorded from the mangrove ecosystems of Uran (Raigad), Navi Mumbai,Maharashtra.At present, coastal environment of Uran shows moderate mangrove density but in coming few years, area around Uran coast will be dominated by intense industrialization and urbanization. In such circumstances, pollution of Uran coast cannot be ignored. Therefore, data presented in this paper can be taken as a base line data for better management of these natural resources.
Key words: Mangroves diversity, Uran, Navi Mumbai,Maharashtra
Communication of Brisset Elodie et al. 2018 in the European Association of Ar...ELODIE BRISSET
Abstract #: 4983 - European Association of Archaeologists 2018
BARCELONA (SPAIN)
RECONSTRUCTION AND IMPACT OF SEASCAPE EVOLUTION ON HUMAN COMMUNITIES DURING THE MESOLITHIC-NEOLITHIC TRANSITION IN THE MEDITERRANEAN IBERIA
Dr. Elodie Brisset, Dr Javier Fernández-López de Pablo, Dr Francesc Burjachs
Institut Català de Paleoecologia Humana i Evolució Social (Spain)
Corresponding author's e-mail: elodie.brisset@imbe.fr
The study of past interactions between hunter-gatherer communities and coastal environment is of major interest because this period was characterised by a rapid sealevel
rise following the Deglaciation. Here we present a study case of Pego-Oliva (Eastern Spain), an area which provides a thick Early-middle Holocene sedimentary infill, together with an extended Mesolithic sequence (El Collado site). Both records provide an unique opportunity to address how the Early Holocene sea level the reduction of coastal plains and the modification of coastal biotopes affected human settlement patterns during the Mesolithic period and the Mesolithic-Neolithic trantition. New fieldwork in the Pego-Oliva lagoon has been carried out in the context of the research project MedCoRes (H2020-MSCA-IF-2015 Ref. 704822). An extensive sampling strategy, based on 3 transects of 16 boreholes covering the Holocene sedimentary infilling, has been implementd together with sedimentological (lithostratigraphy, grainsize, LOI, dry density), and chronostratigraphic analyses (14C dates). This work has allowed to reconstruct three main phases of the morphogenetic evolution: First, from 9800 to 8200 cal. BP, the retrogradational architecture is characterised by four steps of shallow inner lagoon environments associated to sand barriers. Then, from 8200 to 7000 cal. BP, the continuous and rapid backward migration of the shoreline reached its maximal inland position leading to the disappearance of former inner lagoons. Finally, since 7000 cal. BP, sea-level stabilisation promoted the barrier construction leading to formation of an inner coastal lagoon isolated of the sea. Finally, based on paleogeographical reconstructions and radiocarbon modelling we estimated that horizontal inland migration of the coastline reached rates of ~150 m per 50 years. Those results are compared to the Bayesian chronostratigraphy and bioarchaeological assemblages of El Collado. Altogether, our results show synchronic changes of coastal palaeoenvironments and subsistence patterns, arguing that new
strategies have been essential to adapt to highly changing landscapes.
Coastal environment, Mesolithic, Mediterranean, resources
Note/comment
So we were tasked to write scientific papers about the five ecosystems which we have sampled namely: Forest, Grassland, Stream, Coastal Marine, and Mangrove Ecosystems. But then since it was such a handful assignment, our teacher agreed that we can pick only two of these ecosystems that we'll make a scientific paper about and I chose Grassland and Coastal Marine Ecosystems.
FLORAL DIVERSITY OF MANGROVE ECOSYSTEM FROM COASTAL ENVIRONMENT OF URAN (RAIG...Prabhakar Pawar
Mangrove forests are among the world’s most productive ecosystems and are the only forests situated at the confluence of land and sea in tropical and subtropical latitudes.Mangroves are one of the biologically diverse ecosystems in the world, rich in organic matter and nutrients and support very large biomass of flora and fauna. With continuing degradation and destruction ofmangroves, there is a critical need to understand the biodiversity of the mangrove ecosystems.Mangroves represent spirit of Mumbai and NaviMumbai - they are plucky survivors. Each day, millions of citizens in Mumbai pass these hardy plants imaging they are little more than dirty, muddy weeds growing pointlessly along the shoreline. Overexploitation and unsustainable demand has resulted in considerable degradation of mangrove areas and it is feared that the area under mangroves around Mumbai areas has dwindled by 35% in the last 25 years and only about 20 Km2 of mangroves exist today. During this study, 4 species of true
mangroves representing 3 genera and 3 families, 10 species of mangrove associates belonging to 8 genera and 6 families and 1 species of non-mangrove halophytes were recorded from the mangrove ecosystems of Uran (Raigad), Navi Mumbai,Maharashtra.At present, coastal environment of Uran shows moderate mangrove density but in coming few years, area around Uran coast will be dominated by intense industrialization and urbanization. In such circumstances, pollution of Uran coast cannot be ignored. Therefore, data presented in this paper can be taken as a base line data for better management of these natural resources.
Key words: Mangroves diversity, Uran, Navi Mumbai,Maharashtra
Communication of Brisset Elodie et al. 2018 in the European Association of Ar...ELODIE BRISSET
Abstract #: 4983 - European Association of Archaeologists 2018
BARCELONA (SPAIN)
RECONSTRUCTION AND IMPACT OF SEASCAPE EVOLUTION ON HUMAN COMMUNITIES DURING THE MESOLITHIC-NEOLITHIC TRANSITION IN THE MEDITERRANEAN IBERIA
Dr. Elodie Brisset, Dr Javier Fernández-López de Pablo, Dr Francesc Burjachs
Institut Català de Paleoecologia Humana i Evolució Social (Spain)
Corresponding author's e-mail: elodie.brisset@imbe.fr
The study of past interactions between hunter-gatherer communities and coastal environment is of major interest because this period was characterised by a rapid sealevel
rise following the Deglaciation. Here we present a study case of Pego-Oliva (Eastern Spain), an area which provides a thick Early-middle Holocene sedimentary infill, together with an extended Mesolithic sequence (El Collado site). Both records provide an unique opportunity to address how the Early Holocene sea level the reduction of coastal plains and the modification of coastal biotopes affected human settlement patterns during the Mesolithic period and the Mesolithic-Neolithic trantition. New fieldwork in the Pego-Oliva lagoon has been carried out in the context of the research project MedCoRes (H2020-MSCA-IF-2015 Ref. 704822). An extensive sampling strategy, based on 3 transects of 16 boreholes covering the Holocene sedimentary infilling, has been implementd together with sedimentological (lithostratigraphy, grainsize, LOI, dry density), and chronostratigraphic analyses (14C dates). This work has allowed to reconstruct three main phases of the morphogenetic evolution: First, from 9800 to 8200 cal. BP, the retrogradational architecture is characterised by four steps of shallow inner lagoon environments associated to sand barriers. Then, from 8200 to 7000 cal. BP, the continuous and rapid backward migration of the shoreline reached its maximal inland position leading to the disappearance of former inner lagoons. Finally, since 7000 cal. BP, sea-level stabilisation promoted the barrier construction leading to formation of an inner coastal lagoon isolated of the sea. Finally, based on paleogeographical reconstructions and radiocarbon modelling we estimated that horizontal inland migration of the coastline reached rates of ~150 m per 50 years. Those results are compared to the Bayesian chronostratigraphy and bioarchaeological assemblages of El Collado. Altogether, our results show synchronic changes of coastal palaeoenvironments and subsistence patterns, arguing that new
strategies have been essential to adapt to highly changing landscapes.
Coastal environment, Mesolithic, Mediterranean, resources
Note/comment
So we were tasked to write scientific papers about the five ecosystems which we have sampled namely: Forest, Grassland, Stream, Coastal Marine, and Mangrove Ecosystems. But then since it was such a handful assignment, our teacher agreed that we can pick only two of these ecosystems that we'll make a scientific paper about and I chose Grassland and Coastal Marine Ecosystems.
This is presentation that talks about various forest ecosystems and flora and fauna prevailing there. It has simple language, points format and tabular columns for easy understanding. It also contains pictures.
Grassland Ecosystem- As the name implies, grasslands are open spaces in which a variety of grasses grow, with only a few trees scattered near rivers and streams. The amount of annual rainfall influences the type of vegetation – not enough to support a forest but enough to prevent it from becoming a desert. Grasslands are found on every continent except Antarctica.
Grasslands are known in different regions of the world by different names – prairies, pampas, steppes, and savannah among others. They are divided into two types – Tropical and Temperate.
DSD-INT 2019 DANUBIUS-RI the Scientific Agenda-BradleyDeltares
Presentation by Chris Bradley (University of Birmingham, United Kingdom), at the DANUBIUS Modelling Workshop, during Delft Software Days - Edition 2019. Friday, 8 November 2019, Delft.
The Value of Nature - The National Ecosystem Assessment
Dr Megan Tierney, Programme Officer, Ecosystem Assessment Programme, UNEP-WCMC
Andrew Church, Professor of Human Geography, University of Brighton
The Ecology and Ecosystems unit notes blend in Evolutionary adaptations and Evidence for Evolution along with standard E&E topics. The notes has examples of key content areas. Originally designed for Junior High and High School students, we use these for 7-8th grade students and warm ups for High School students. Includes basic concepts, food chain, webs, energy pyramids, matter cyclers, predator-prey, trophic levels; along with Ecosystem types, carrying capacity as well as Rules of the Environment.
In this presentations, structure of ecosystems, food chain, food web, ecological pyramids, energy flow, biogeochemical cycles of nitrogen and phosphorus is explained.
assessing heterogeneous influences on partial deposition of virus in lateriticIJCMESJOURNAL
This paper monitored the rate of partial deposition of virus on heterogeneous formation, the study were able to monitor the behaviour of virus in heterogeneous deposition influencing partial concentration of virus in Lateritic and silty formation. The study was able to observe the rate of partial deposition base on its rate of fluctuation through variation observed from deposited void ratio and permeability, such formation developed fluctuation on these parameters thus generated partial deposition of virus in the study area. Linear deposition were also experienced in graphical representation, the result obtained ranged from [1.97E-12-2.35E-11],[3-30M], [1.97E-12-2.36E-11[10-100] Predictive 1.97E-12, Experimental 1.87E-12 [3-36m], predictive, [1,97E-12], Experimental [2.26E-11] [10-120 Days] predictive 2.36E-12, Experimental 2.24E-11,[10-120Days] [1.31E-12-2.36E11], Predictive1.31E-12, Experimental, 2.36E-11 [2-30m], predictive,[2.36E-11-2.2E-11]; [2-30m] ,for Time 1.31E-12-2.36E-11[4-60days] while predictive and Experimental,[2,36E-11] [1.37E-12-2,22E-11] [2-30m] The prediction rate of partial deposition of virus was possible through mathematical modeling techniques, the system were developed base on the parameters from predominant formation characteristics in study location, these parameters generated the derived model through the developed governing equation, simulation generated theoretical values that were compared with experimental results, both parameters developed best fits validating the model, experts will definitely applied this approach in monitoring and evaluation of virus deposits in the study area.
assessing heterogeneous influences on partial deposition of virus in lateriticIJCMESJOURNAL
This paper monitored the rate of partial deposition of virus on heterogeneous formation, the study were able to monitor the behaviour of virus in heterogeneous deposition influencing partial concentration of virus in Lateritic and silty formation. The study was able to observe the rate of partial deposition base on its rate of fluctuation through variation observed from deposited void ratio and permeability, such formation developed fluctuation on these parameters thus generated partial deposition of virus in the study area. Linear deposition were also experienced in graphical representation, the result obtained ranged from [1.97E-12-2.35E-11],[3-30M], [1.97E-12-2.36E-11[10-100] Predictive 1.97E-12, Experimental 1.87E-12 [3-36m], predictive, [1,97E-12], Experimental [2.26E-11] [10-120 Days] predictive 2.36E-12, Experimental 2.24E-11,[10-120Days] [1.31E-12-2.36E11], Predictive1.31E-12, Experimental, 2.36E-11 [2-30m], predictive,[2.36E-11-2.2E-11]; [2-30m] ,for Time 1.31E-12-2.36E-11[4-60days] while predictive and Experimental,[2,36E-11] [1.37E-12-2,22E-11] [2-30m] The prediction rate of partial deposition of virus was possible through mathematical modeling techniques, the system were developed base on the parameters from predominant formation characteristics in study location, these parameters generated the derived model through the developed governing equation, simulation generated theoretical values that were compared with experimental results, both parameters developed best fits validating the model, experts will definitely applied this approach in monitoring and evaluation of virus deposits in the study area.
Characterization and the Kinetics of drying at the drying oven and with micro...Open Access Research Paper
The objective of this work is to contribute to valorization de Nephelium lappaceum by the characterization of kinetics of drying of seeds of Nephelium lappaceum. The seeds were dehydrated until a constant mass respectively in a drying oven and a microwawe oven. The temperatures and the powers of drying are respectively: 50, 60 and 70°C and 140, 280 and 420 W. The results show that the curves of drying of seeds of Nephelium lappaceum do not present a phase of constant kinetics. The coefficients of diffusion vary between 2.09.10-8 to 2.98. 10-8m-2/s in the interval of 50°C at 70°C and between 4.83×10-07 at 9.04×10-07 m-8/s for the powers going of 140 W with 420 W the relation between Arrhenius and a value of energy of activation of 16.49 kJ. mol-1 expressed the effect of the temperature on effective diffusivity.
Diabetes is a rapidly and serious health problem in Pakistan. This chronic condition is associated with serious long-term complications, including higher risk of heart disease and stroke. Aggressive treatment of hypertension and hyperlipideamia can result in a substantial reduction in cardiovascular events in patients with diabetes 1. Consequently pharmacist-led diabetes cardiovascular risk (DCVR) clinics have been established in both primary and secondary care sites in NHS Lothian during the past five years. An audit of the pharmaceutical care delivery at the clinics was conducted in order to evaluate practice and to standardize the pharmacists’ documentation of outcomes. Pharmaceutical care issues (PCI) and patient details were collected both prospectively and retrospectively from three DCVR clinics. The PCI`s were categorized according to a triangularised system consisting of multiple categories. These were ‘checks’, ‘changes’ (‘change in drug therapy process’ and ‘change in drug therapy’), ‘drug therapy problems’ and ‘quality assurance descriptors’ (‘timer perspective’ and ‘degree of change’). A verified medication assessment tool (MAT) for patients with chronic cardiovascular disease was applied to the patients from one of the clinics. The tool was used to quantify PCI`s and pharmacist actions that were centered on implementing or enforcing clinical guideline standards. A database was developed to be used as an assessment tool and to standardize the documentation of achievement of outcomes. Feedback on the audit of the pharmaceutical care delivery and the database was received from the DCVR clinic pharmacist at a focus group meeting.
WRI’s brand new “Food Service Playbook for Promoting Sustainable Food Choices” gives food service operators the very latest strategies for creating dining environments that empower consumers to choose sustainable, plant-rich dishes. This research builds off our first guide for food service, now with industry experience and insights from nearly 350 academic trials.
UNDERSTANDING WHAT GREEN WASHING IS!.pdfJulietMogola
Many companies today use green washing to lure the public into thinking they are conserving the environment but in real sense they are doing more harm. There have been such several cases from very big companies here in Kenya and also globally. This ranges from various sectors from manufacturing and goes to consumer products. Educating people on greenwashing will enable people to make better choices based on their analysis and not on what they see on marketing sites.
"Understanding the Carbon Cycle: Processes, Human Impacts, and Strategies for...MMariSelvam4
The carbon cycle is a critical component of Earth's environmental system, governing the movement and transformation of carbon through various reservoirs, including the atmosphere, oceans, soil, and living organisms. This complex cycle involves several key processes such as photosynthesis, respiration, decomposition, and carbon sequestration, each contributing to the regulation of carbon levels on the planet.
Human activities, particularly fossil fuel combustion and deforestation, have significantly altered the natural carbon cycle, leading to increased atmospheric carbon dioxide concentrations and driving climate change. Understanding the intricacies of the carbon cycle is essential for assessing the impacts of these changes and developing effective mitigation strategies.
By studying the carbon cycle, scientists can identify carbon sources and sinks, measure carbon fluxes, and predict future trends. This knowledge is crucial for crafting policies aimed at reducing carbon emissions, enhancing carbon storage, and promoting sustainable practices. The carbon cycle's interplay with climate systems, ecosystems, and human activities underscores its importance in maintaining a stable and healthy planet.
In-depth exploration of the carbon cycle reveals the delicate balance required to sustain life and the urgent need to address anthropogenic influences. Through research, education, and policy, we can work towards restoring equilibrium in the carbon cycle and ensuring a sustainable future for generations to come.
Artificial Reefs by Kuddle Life Foundation - May 2024punit537210
Situated in Pondicherry, India, Kuddle Life Foundation is a charitable, non-profit and non-governmental organization (NGO) dedicated to improving the living standards of coastal communities and simultaneously placing a strong emphasis on the protection of marine ecosystems.
One of the key areas we work in is Artificial Reefs. This presentation captures our journey so far and our learnings. We hope you get as excited about marine conservation and artificial reefs as we are.
Please visit our website: https://kuddlelife.org
Our Instagram channel:
@kuddlelifefoundation
Our Linkedin Page:
https://www.linkedin.com/company/kuddlelifefoundation/
and write to us if you have any questions:
info@kuddlelife.org
Micro RNA genes and their likely influence in rice (Oryza sativa L.) dynamic ...Open Access Research Paper
Micro RNAs (miRNAs) are small non-coding RNAs molecules having approximately 18-25 nucleotides, they are present in both plants and animals genomes. MiRNAs have diverse spatial expression patterns and regulate various developmental metabolisms, stress responses and other physiological processes. The dynamic gene expression playing major roles in phenotypic differences in organisms are believed to be controlled by miRNAs. Mutations in regions of regulatory factors, such as miRNA genes or transcription factors (TF) necessitated by dynamic environmental factors or pathogen infections, have tremendous effects on structure and expression of genes. The resultant novel gene products presents potential explanations for constant evolving desirable traits that have long been bred using conventional means, biotechnology or genetic engineering. Rice grain quality, yield, disease tolerance, climate-resilience and palatability properties are not exceptional to miRN Asmutations effects. There are new insights courtesy of high-throughput sequencing and improved proteomic techniques that organisms’ complexity and adaptations are highly contributed by miRNAs containing regulatory networks. This article aims to expound on how rice miRNAs could be driving evolution of traits and highlight the latest miRNA research progress. Moreover, the review accentuates miRNAs grey areas to be addressed and gives recommendations for further studies.
Willie Nelson Net Worth: A Journey Through Music, Movies, and Business Venturesgreendigital
Willie Nelson is a name that resonates within the world of music and entertainment. Known for his unique voice, and masterful guitar skills. and an extraordinary career spanning several decades. Nelson has become a legend in the country music scene. But, his influence extends far beyond the realm of music. with ventures in acting, writing, activism, and business. This comprehensive article delves into Willie Nelson net worth. exploring the various facets of his career that have contributed to his large fortune.
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Introduction
Willie Nelson net worth is a testament to his enduring influence and success in many fields. Born on April 29, 1933, in Abbott, Texas. Nelson's journey from a humble beginning to becoming one of the most iconic figures in American music is nothing short of inspirational. His net worth, which estimated to be around $25 million as of 2024. reflects a career that is as diverse as it is prolific.
Early Life and Musical Beginnings
Humble Origins
Willie Hugh Nelson was born during the Great Depression. a time of significant economic hardship in the United States. Raised by his grandparents. Nelson found solace and inspiration in music from an early age. His grandmother taught him to play the guitar. setting the stage for what would become an illustrious career.
First Steps in Music
Nelson's initial foray into the music industry was fraught with challenges. He moved to Nashville, Tennessee, to pursue his dreams, but success did not come . Working as a songwriter, Nelson penned hits for other artists. which helped him gain a foothold in the competitive music scene. His songwriting skills contributed to his early earnings. laying the foundation for his net worth.
Rise to Stardom
Breakthrough Albums
The 1970s marked a turning point in Willie Nelson's career. His albums "Shotgun Willie" (1973), "Red Headed Stranger" (1975). and "Stardust" (1978) received critical acclaim and commercial success. These albums not only solidified his position in the country music genre. but also introduced his music to a broader audience. The success of these albums played a crucial role in boosting Willie Nelson net worth.
Iconic Songs
Willie Nelson net worth is also attributed to his extensive catalog of hit songs. Tracks like "Blue Eyes Crying in the Rain," "On the Road Again," and "Always on My Mind" have become timeless classics. These songs have not only earned Nelson large royalties but have also ensured his continued relevance in the music industry.
Acting and Film Career
Hollywood Ventures
In addition to his music career, Willie Nelson has also made a mark in Hollywood. His distinctive personality and on-screen presence have landed him roles in several films and television shows. Notable appearances include roles in "The Electric Horseman" (1979), "Honeysuckle Rose" (1980), and "Barbarosa" (1982). These acting gigs have added a significant amount to Willie Nelson net worth.
Television Appearances
Nelson's char
Natural farming @ Dr. Siddhartha S. Jena.pptxsidjena70
A brief about organic farming/ Natural farming/ Zero budget natural farming/ Subash Palekar Natural farming which keeps us and environment safe and healthy. Next gen Agricultural practices of chemical free farming.
1. Environmental Ecology Lab
Stream Ecology:
Density Independence Versus Density
Dependence In Streams
Presented By- Mamun Md.
Master’s Degree
Dept.- Bioscience and Biotechnology
Major Field-Biodiversity and Environmental Ecology
Student Id-201650783
Session -2016,Spring
2. Environmental Ecology Lab
Contents:
Introduction
Characterization of Stream systems
Objectives
Density Independent Mechanism
Density Dependent Mechanism
Density-dependent factors
Density-independent factors
Implication of density dependence
Existence of density dependent factors in stream systems
Experimental evaluation of various density dependent
mechanisms in stream systems
Support density independent regulation as the major factor
regulating organisms in stream systems by Researchers
Dominance of Density Independence – Is It valid?
3. Environmental Ecology Lab
Contents:
Testing Stream Systems for Density Regulating Mechanisms
Functional group concept
How density dependence can conduct by using Grazers?
Several Problems arise during study of density dependent
interactions by using grazers
Mechanisms of detritus in stream ecosystems
Stream detrital dynamics model
Conclusion
4. Environmental Ecology Lab
Introduction:
♣ Descriptive Science
♣ Taxonomy has been a major thrust
♣ Describe basic structure of stream communities
♣ Life histories of some species
♣ Examine functional relationships within stream community
♣ Formalization of the functional group concept, RCC concept
♣ Recognition the importance of detritus and instream autotrophy
5. Environmental Ecology Lab
Characterization of stream systems:
♣ Annual floods
♣ Occasional catastrophic floods
♣ Pulsed periods of detrital input
♣ Seasonal temperature changes
bed of the stream is subject to both erosion and deposition
8. Environmental Ecology Lab
Density independent mechanism:
♣ Catastrophic mechanism which act independently of the density
of the population being affected
♣ Like, a spate or sudden freeze
♣ After passing that event population contain exponential growth.
Density dependent mechanism:
♣ Change in intensity as a function of population density
♣ Like, predation , competition and parasitism.
♣ When the population increases , the influence of density
dependent mechanisms also increases
♣ Reduction in population growth = intrinsic rate of population’s
growth
9. Environmental Ecology Lab
Density-dependent factors:
A factor that depends on population size is called a density-
dependent factor.
Density-dependent factors include:
♣ Competition
♣ Predation
♣ Parasitism
♣ Disease
♣ Territoriality
♣ Waste Accumulation
♣ Migration
10. Environmental Ecology Lab
Density-independent factors:
Density-independent factors affect all populations in similar
ways, regardless of the population size.
Examples of density-independent factors
include:
♣ Unusual Weather
♣ Natural Disasters
♣ Seasonal Cycles
♣ Certain Human Activities—such As Damming Rivers
And Clear-cutting Forests
♣ Fire
♣ Flood Weather
♣ Volcanic Eruption
♣ Chemical Pesticides
11. Environmental Ecology Lab
Implication of density dependence:
♣ Population is controlled by food supplies or floods
♣ Concern reproductive strategies, diversity and the general
applicability of equilibrium based ecological theory
♣ More applied scale – management strategies , impact
assessment and prediction
♣ Assemblages of opportunists rearrange the community
structure( Paine, 1966,1669)
12. Environmental Ecology Lab
Existence of density dependent factors in stream
systems:
♣ Impact of predaceous flatworms in restructuring a stream
community ( Macan,1962)
♣ Factors influencing the distribution of lotic Trichoptera
(Edington, 1965)
♣ Physical factors set as distributional template and territorial
behavior was the ultimate regulating mechanism(Edington, 1965)
♣ Support the competitive exclusion principle(Allan, 1975)
♣ Microhabitat segregation found between two congeneric
harpacticoid copepods (Shiozawa,1978)
13. Environmental Ecology Lab
Experimental evaluation of various density
dependent mechanisms in stream systems:
♣ Manipulation of invertebrate in cages and conclude that
movements were density dependent (Peckarsky,1979)
♣ Competitive interactions among benthic grazers (McAuliffe and
Hart)
♣ Found significant differences in leaf pack decomposition
rates(Oberndorfer et.al)
♣ Perhaps the best known working hypothesis is the excess
production hypothesis(Waters 1961, 1965, 1966)
14. Environmental Ecology Lab
♣ Excess production hypothesis relates behavioral drift to
assimilation and secondary production above the carrying
capacity
♣ Manipulated food level in artificial streams and significantly
found more drift with lower concentrations(Hildebrand, 1974)
♣ No significant change in stream benthos after trout were
excluded from Colorado stream (Allan, this volume)
15. Environmental Ecology Lab
Support density independent regulation as the
major factor regulating organisms in stream
systems by Researchers:
♣ Factors controlling benthic invertebrates in running waters and
90% discussion was density independent
mechanisms(Hynes,1970)
♣ No community of running water may considered as climax and
a climax community implies equilibrium conditions and Violence
of flow is the main regulatory mechanisms(Margalef, 1960)
♣Headwater stream communities as assemblages of
opportunists(Patrick,1972)
♣ Opportunists inhabits in headwater streams of temperate
area(Stout and Vandermeer,1975)
17. Environmental Ecology Lab
Yes , it is valid due to four reasons.
1. Major factor regulating stream community structure
2. High diversity that exists in temperate streams
3. Support highly variable distribution of stream benthos
4. Predominantly a descriptive science
18. Environmental Ecology Lab
1. Major factor regulating stream community
structure:
♣ Effects of three catastrophic floods caused major restructuring
of the stream ecosystems( Hynes, 1972)
♣ Snow melt with ice jam effect downstream community
structure in several kilometers( Shiowzawa)
♣Summer cloud bursts caused catastrophic changes in
community structure
♣Long term dynamics of a single community is nonexistent and
density dependence , like density independence ,need to operate
continually(macArthur,1972; Wiens,1977)
19. Environmental Ecology Lab
2. High diversity that exists in temperate
streams:
♣ Diversity may develop from a patchy environment induced by
density independent factors
♣ Few major contradictions noted by MacArthur when compare
with tropical diversity
♣ Inferior species increase the community diversity
♣ Intermediate disturbances are important factors in controlling
diversity in both tropical coral reefs and tropical forests and
undergoing succession by uncolonized cells or patches
( Connell,1978and 1979)
20. Environmental Ecology Lab
3. Support highly variable distribution of stream
benthos :
♣ Support correlative field relationship depend on physical
factors
♣ Most familiar example , sampled a “ relatively uniform riffle “
and estimate community density with 95% Confidence(Needham
and Usinger, 1956)
♣ Improved the quantitative nature of sampling gear( Waters and
knapp,1961; Mundie ,1971)
♣ Refined statistical methodology(Elliott,1977)
♣Benthic sampling depend on plot type sampling technique ,one
square foot
21. Environmental Ecology Lab
♣ Increasing the area during sampling on heterogeneous
conditions improved the precision of Data
♣ processing of samples in the laboratory can be simplified by
statistics( Cochran,1963;green ,1979 et.al) and equipment
(Waters,1969;Mundie 1971)
♣ Plotless techniques ( Shiozawa,1978) and reduced sampler
area improve resolution of habitat grain (Elliott,1977)
22. Environmental Ecology Lab
4. Predominantly a descriptive science:
♣ Basic approach is sample survey
♣ sample numbers converted to densities or biomass and give a
picture about stream community structure
♣ After advent of computer and statistical packages data seta
gain more validity and interpretations obtain more legitimacy
23. Environmental Ecology Lab
Two basic problems arise with statistical
methodology:
♣ First, As we measure the parameters through our intuition
which is biased by our own limited ability in perceiving all
potential causal factors
♣ Stream ecosystems analyzed by using two components .
I. Abiotic components( often field observed)
II. Biotic components( often laboratory derived)
♣ Second, Sampling survey can not prove causality
♣ Statistics based on sample surveys do not make definitive
conclusions about causality
24. Environmental Ecology Lab
Testing Stream Systems for Density Regulating
Mechanisms:
♣ Formulation of logical hypotheses
♣Mathematical modelling(give precise predictions and
opportunity of formulating biological relationships and observing
“noiseless “ system changes according to these relationships)
How hypotheses can be tested?
♣ Very extensive sampling-type surveys
♣ Experimental manipulation
Experimental manipulation is probably the best approach for
the stream researchers
Here causality can be demonstrated
25. Environmental Ecology Lab
How benthic community regulated by the
factors?
♣ Not all members of the benthic community are regulated by
the same factors
♣some are regulated by predation , others by food , space or
density independent factors
♣ The community include organisms of different trophic levels
and different functional groups( Cummins,1974;cummins and
Klug,1979) across these levels
♣In a community the manipulation of one factor may only
influence a few species and the other species might show no
effect
26. Environmental Ecology Lab
Functional group concept:
♣ Functional designations are mutable(Merritt and
Cummins,1978)
♣Organisms may specialize differentially within separate
communities( Fox and Morrow,1981) and thus have different
functional roles in those communities.
♣Within a community a given species may perform several
functions
27. Environmental Ecology Lab
How density dependence can conduct by using
Grazers?
♣High densities of mountain suckers (Pantosteus platyrhynchus)
occurred in some pools and were in low densities in others in the
Raft River ,Idaho
♣ The riffles adjacent to pools containing high sucker densities
had low filamentous algal cover
♣Mountain suckers are grazers( Scott and Crossman,1973) and
helps in structuring the local algal communities
♣Exclusion of grazers from the tiles resulted in an increase in
algal biomass( Lamberti and Resh,1980)
28. Environmental Ecology Lab
Several Problems arise during study of density
dependent interactions by using grazers:
♣ First, the influence of seasonality on density dependent
interactions
♣ Factors such as canopy, angle of the sun , turbidity and water
temperature vary seasonally and influence the production rate
of autotroph and instream primary production will not remain
constant (Hickman,1974)
♣ Second, many aquatic organisms grow in cohorts
♣ Biomass is confounded with time
29. Environmental Ecology Lab
Use of production rates avoid these two
problems:
♣ Excess production hypothesis not only invokes density
dependence as a regulating mechanism, but also converts the
mechanism into one related to energy flow and production
♣ Drift acts as a mortality factor
♣Probability of mortality is higher in drifters
(Allan,1978;Waters,1972)
♣ Measurement of primary and secondary production is not
easy and normally conducted in unmanipulated field conditions
30. Environmental Ecology Lab
Mechanisms of detritus in stream ecosystems:
♣ Most detritus is introduced in Autumn leaf fall in stream in
temperate climates
♣ Leaves are colonized and turn into food for detritivores
(Cummins,1974)
♣ Carrying capacities increase by annual pulsing of leaf litter
♣ Subsequent increase of CPOM and then transfer into MPOM
and FPOM , respectively and then into DOM
♣ Leachate and other DOM flocculate (Lock and Hynes, 1975 and
1976) and make up a significant portion of fines(Boling
et.al.,1975)
31. Environmental Ecology Lab
♣ FPOM fluctuate annually ( Hynes et.al., 1974)
♣ High degree of age and species specificity in the filter net size
implies some degree of specialization to the food resources being
exploited ( Wallace et al., 1977)
♣ Periods of food scarcity (Weins,1977) are most likely to occur
during the periods of decline of the pulses
♣Shredder community can also be predicted by using K of leaf
material
32. Environmental Ecology Lab
Stream detrital dynamics model:
♣Predict changes in leaf standing stock with different storage
capacities of the stream systems
♣ Rate of leaf decomposition in a stream is related to factors like
leaf species, shredder abundance , water temperature and
location of the leaf material in the stream(cummins et.al;1973
and so on.
♣ if detritus decomposition and processing is location specific
(Meyer,1980) then the standing stock of leaf material will be a
function of the diversity locations.
♣ Decomposition slower in reducing environments
♣ depositional regions(pools) contain low amount of oxygen but
erosional regions(riffles) contain high amount of oxygen because
of turbulence
33. Environmental Ecology Lab
♣ Simulation was run with continuous litter input and the
results behave as anticipated (Fig.1 and 2)
♣ Low riffle ratio (high pool) stored more material than
the high riffle system
♣ Litter input is pulsed , not continuous and the levels of
material resulting in streams with differing storage
capacities
34. Environmental Ecology Lab
♣ A simple function(Dixon,1976) was used which allowed a
changing rate of leaf fall ( Fig.3)
♣ Systems with high proportions of riffles tend to have more
pulsed leaf litter standing stock in the areas. Input of the leaves
from terrestrial system and subsequent leakage is dominant
(Fig.4)
♣Systems with low riffle ratio (Fig.5) and high pool ratios have
less pulsed leaf litter standing stocks
♣ impact of leakage from the system is buffered by leakage to
the riffle from the pool storage(Fig.6)
35. Environmental Ecology Lab
♣ This model is still being modified and data collected from
valley Creek, Minnesota and have some assumptions
♣ While general predictions are still accommodated, storage
capacities and leakage rates differ more than originally assumed
♣ These variations will probably increase the differences
between riffle –pool ratios rather than diminish them
36. Environmental Ecology Lab
♣ Density dependence will be more likely in the high riffle ratio
systems
♣ Here leaves for shredding should become limiting rapidly
♣ High storage capacity streams have more gradual leakage to
the riffles
♣Assimilation ratio of riffles to pools related to total secondary
production rates
♣Increased secondary production from increased riffle area may
reduced storage capacity of stream
37. Environmental Ecology Lab
♣ Leaf pack decomposition approximates a negative exponential
curve(Petersen and Cummins,1974)
♣ If leaf pack size sets K, K will eventually approach zero
♣ Shredder curve shows an initial colonization pulse and
subsequently , smoothly tracks the declining K
♣ Drift occurs in a diel pattern , the feeding activity patterns of
drifting organisms are likely to be diel also
♣ Oscillations of K depend on microorganisms growth rates with
time and nutrients
38. Environmental Ecology Lab
Conclusion:
♣ Streams are complex systems
♣ Their complexity does not make them
impossible subjects for study of density
dependent and independent factors
♣ It based on sound hypothesis and
experimental design
Thank you for kind attention