Chapter 5 Notes: From Ecosystems to Biomes

Ecosystems

  • Ecosystems are dynamic networks where living communities interact with abiotic factors and energy/nutrient flows.

  • Key ecosystem processes include photosynthesis, respiration, energy flow, and nutrient cycling.

  • Humans rely on ecosystems and assign value to ecosystem goods and services (external benefits).

  • Abiotic factors and biotic interactions set the range of tolerance and limiting factors that determine species distributions.

  • Ecosystems contain communities of interacting species and their physical environment; predictable patterns of ecosystem distribution exist globally.

  • Biomes are ecosystems with similar vegetation and climatic conditions; they represent broad geographic patterns rather than strict boundaries.


Trophic levels

  • In photosynthesis, plants use light energy, CO₂, and H₂O to produce organic molecules (sugar). The general equation for photosynthesis can be written as:
    6\,CO{2} + 6\,H{2}O + \text{light energy} \rightarrow C{6}H{12}O{6} + 6\,O{2}

  • Energy and nutrients flow up through trophic levels (feeding levels) as organisms consume others.

  • A trophic level is defined by the primary source of energy for that level; energy and materials move upward through the system.

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Food chains and food webs

  • Food chain: describes the linear transfer of energy and nutrients from one organism to another; energy generally moves upward through the chain.

  • Not all energy/nutrients reach higher trophic levels; much is lost at each step.

  • Food web: a network of interconnected food chains forming complex feeding relationships, usually more evident in aquatic systems.


Aquatic food webs (illustrative components)

  • Common components across Arctic and marine systems include:

    • Producers: phytoplankton, diatoms, photosynthetic/chemosynthetic autotrophs.

    • Primary consumers: herbivorous zooplankton, small fish.

    • Secondary/tertiary consumers: arctic cod, ringed seals, bearded seals, bowhead whale, polar bear, arctic fox, beluga whale, etc.

    • Carnivorous zooplankton; detritivores and decomposers are also part of the web.

  • Aquatic webs often feature ice biota (diatoms) and marine/estuarine linkages; these webs illustrate energy flow and trophic interactions in aquatic environments.


Autotrophs and heterotrophs (basics)

  • Autotrophs: produce organic matter (OM) from inorganic matter using external energy sources.

    • Producers: green plants (photosynthetic) and chemotrophic bacteria.

  • Heterotrophs: consume OM to obtain energy.

    • Consumers: eat living prey; include primary (herbivores), secondary, tertiary, and higher-order consumers.

    • Decomposers: scavengers, detritus feeders, and chemical decomposers that break down dead OM.


Producers and primary production

  • Photosynthesis captures light energy to convert CO₂ and H₂O to OM.

  • Chlorophyll is the green pigment responsible for absorbing light energy.

  • Chemosynthesis allows bacteria to use energy from inorganic chemicals (e.g., H₂S, NH₃) to synthesize OM.

  • Primary production (also called primary productivity) is the production of OM through photosynthesis and associated biomass growth.


Global primary productivity (terrestrial)

  • Net Primary Production (NPP): the classified rate of new plant biomass production (tonnes of dry organic matter per hectare per year) for ecosystems.

  • Units and scale (terrestrial): often presented as tons/ha/year of total dry matter (above- and below-ground).

  • Values vary by ecosystem type; general ranges observed include None, Low (~1), and High (~15) for reference scales in teaching materials.


Consumers

  • Consumers include animals, fungi, and many bacteria; they are categorized by food source:

    • Primary consumers (herbivores): feed on producers.

    • Secondary consumers (carnivores): feed on primary consumers.

    • Tertiary and higher-order consumers.

  • Carnivores are typically secondary or higher-order meat eaters.

  • Omnivores feed on both plants and animals.


Grassland food chain (illustrative structure)

  • Producers → First-level (primary) consumer → Second-level (secondary) consumer → Third-level (tertiary) consumer

  • This simple chain represents the flow of energy from producers up through consumers; each ascending level typically contains less biomass.


Decomposers and detritus

  • Decomposers convert detritus (dead plant material, waste, and bodies) back into inorganic forms and energy.

  • Detritus is high in potential energy and fuels detritivores and chemical decomposers.

  • Detritus-based pathways are especially important in nutrient cycling.

  • Key decomposer groups:

    • Scavengers (e.g., vultures) break down large pieces of matter.

    • Detritus feeders (e.g., earthworms) feed on partly decomposed matter.

    • Chemical decomposers (e.g., fungi and bacteria) break down molecule-sized matter.


Specialized decomposers and microbial pathways

  • Some decomposers digest wood (cellulose) via mutualisms with gut microorganisms (e.g., termites).

  • Cellulose: plant cell-wall material; humans cannot digest it.

  • Anaerobic respiration occurs in the absence of oxygen (in sediments, guts, etc.).

  • Fermentation is a form of anaerobic respiration used by some decomposers; it breaks down glucose in the absence of oxygen and produces byproducts like ethanol, methane, and acetic acid.


Trophic categories (summary)

  • Autotrophs: make their own organic matter from inorganic nutrients using energy sources.

  • Heterotrophs: must feed on organic matter for energy.

  • Producers:

    • Photosynthetic green plants (chlorophyll)

    • Photosynthetic bacteria (light-absorbing pigments)

    • Chemosynthetic bacteria (oxidation of inorganic chemicals like
      hydrogen sulfide)

  • Consumers:

    • Primary consumers/herbivores: feed on plants

    • Omnivores: feed on both plants and animals

    • Secondary consumers/carnivores: feed on primary consumers

    • Higher-order consumers: feed on other carnivores

  • Parasites: feed on another organism over time

  • Decomposers, scavengers, detritus feeders, chemical decomposers (as defined above)


Limits on trophic levels and biomass pyramids

  • Terrestrial ecosystems typically have 3–4 trophic levels; marine systems can have up to 5.

  • Biomass pyramid concept: the total biomass at higher trophic levels is smaller than that at lower levels, with about a 90% decrease per step.

  • Example relation:
    ext{Biomass}{n+1} \approx 0.1 \times \text{Biomass}n
    or equivalently a ~90% reduction moving up a trophic level.

  • This creates a pyramid shape when biomass is plotted by trophic level.


Biomass pyramid (illustrative description)

  • Producers form the base with the largest biomass.

  • 1st-level consumers (herbivores) have about one-tenth the biomass of producers.

  • 2nd-level consumers (primary carnivores) have about one-tenth the biomass of 1st-level consumers.

  • The biomass at higher levels decreases progressively, forming a pyramid.


Flow of energy and standing-crop biomass (terrestrial)

  • Standing-crop biomass: the biomass of primary producers in an ecosystem at a given time (above-ground focus is common).

  • Biomass and primary production vary greatly by ecosystem type and climate.

    • Forests tend to have large biomass.

    • Grasslands tend to have high primary production.

  • Sunlight is the primary energy source for most ecosystems; primary production uses only about 2\% of available solar energy, yielding roughly 120\ \text{gigatons of OM/year}

  • Note: These numbers illustrate the general scale and efficiency, not exact values for every ecosystem.


Fate of consumed energy and efficiency

  • Of food energy consumed:

    • About 60\%\text{–}90\% is oxidized for energy (maintenance, activities).

    • About 10\%\text{–}40\% is converted to body tissues for growth and repair.

    • Undigested energy leaves as waste.

  • Excretion also removes carbon dioxide, nitrogen, phosphorus, and water.


Energy flow is inefficient and production terminology

  • Only a small fraction of energy passes to the next trophic level; much is not consumed, used in metabolism, or excreted.

  • Secondary production: the rate of growth of consumers over time; energy and matter transfer from lower to higher trophic levels to form new tissue.


Trophic inefficiency and biomagnification

  • Higher trophic levels require more energy to produce the same amount of tissue (greater energy demand).

  • Some materials (e.g., heavy metals, pesticides) are hard to degrade and are excreted slowly; they bioaccumulate within individuals and magnify up the food chain (bioaccumulation and biomagnification).


Aquatic vs. terrestrial systems: key contrasts

  • Aquatic systems follow similar energy flow patterns but with two major differences:
    1) More energy is available at each level; energy transfer is more efficient; cold-blooded (ectothermic) animals require less energy for body mass.
    2) Aquatic systems tend to have a reversed biomass pyramid: smaller biomass of algae/phytoplankton at the base but greater biomass of larger fish higher up, in some contexts.

  • Bottom-up dynamics in aquatic systems can lead to longer chains and different turnover rates; algae and phytoplankton often have rapid growth and turnover, while upper-level organisms live longer and may accumulate biomass.


From ecosystems to biomes: climate and geography

  • Ecosystem patterns have predictable populations of organisms under particular conditions.

  • Regions host distinct biotic communities and know patterns of energy flow and food webs/trophic levels.

  • A biome is a large geographical terrestrial biotic community controlled by climate; often named after dominant vegetation; boundaries are not sharply defined and can vary with time.


Climate and its role in biomes

  • Climate describes average temperature and precipitation (weather) patterns of a region and varies widely.

  • Latitudinal and altitudinal gradients drive climate differences:

    • Equatorial regions: warm, high rainfall, minimal seasons.

    • Temperate regions: seasonal variation with distinct seasons.

    • Polar regions: long, cold winters.

  • The average temperature in a region varies with latitude and altitude.


Latitude, altitude, and microclimates

  • Effects of latitude and altitude shape which biomes occur where:

    • Needleleaf forests, temperate deciduous forests, tropical rain forests, tundra, ice and snow, etc.

  • Microclimates create localized variations within a biome, leading to finer-scale ecosystem differences.


Precipitation and climate suitability

  • Precipitation varies from near zero to >100 inches/year and can be evenly or seasonally distributed.

  • Species persist where temperature and precipitation fall within their tolerance ranges; highest densities occur where conditions are optimal; species are excluded when conditions exceed tolerance limits.


Temperature-delineated biomes

  • Tropical rain forests: broad-leaved evergreens; cannot tolerate freezing.

  • Deciduous forests: trees drop leaves and go dormant in freezing temperatures.

  • Coniferous forests: tolerate harsh winters and short summers in northern regions.

  • Permafrost: permanently frozen subsoil; roots cannot penetrate; tundra biome persists where permafrost is present.


Terrestrial biomes map (conceptual overview)

  • Biome distribution is often depicted across latitude/longitude with zones for tundra, boreal forests, temperate forests, deserts, tropical forests, etc., reflecting patterns of temperature and precipitation.


Aquatic systems: freshwater and marine

  • Aquatic systems are determined by depth, salinity, and permanence of water.

  • Freshwater systems include lakes, marshes, streams, and rivers.

  • Mixed ecosystems (estuaries, bays) occur where fresh and saltwater mix.

  • Marine systems include oceans and coastal regions.


Productivity across biomes

  • Biomes differ in primary productivity; tropical rain forests are highly productive due to warm temperatures and abundant rainfall.

  • Open oceans account for high global productivity due to vast area, but local productivity rates can be low because nutrients are often scarce.

  • Overall, tropical and coastal systems tend to have high productivity; open oceans contribute significantly to global productivity despite lower rate per unit area.

  • Productivity is commonly measured as net primary production (NPP) in units such as \text{g m}^{-2}\text{ yr}^{-1}.


Productivity by ecosystem (conceptual overview)

  • A range of ecosystems show varying NPP values; some examples include algal beds/reefs, tropical rain forests, estuaries, temperate forests, savannas, boreal forests, wetlands, cultivated land, lakes/streams, deserts, and open ocean.

  • Relative rankings typically place tropical rain forests and estuaries/high-nutrient systems among the highest, while deserts and open ocean surface waters can be lower on a per-area basis but contribute substantially to global productivity due to large area.

  • A representative way to compare is by plotting Average annual NPP (g/m²/yr) against the biome’s share of global surface area and its contribution to global NPP.

  • If you need exact numeric values for each biome, refer to the table that lists NPP by biome (values in \text{g m}^{-2}\text{ yr}^{-1}) and corresponding surface-area shares; the table shows tropical forests, algal beds and reefs, estuaries, open ocean, lakes, deserts, tundra, etc., with a wide range across biomes.


Ecosystem disturbance and resilience

  • An ecosystem experiences disturbances (natural or human-caused) that interrupt ecological succession and create new conditions on site (e.g., volcanoes, fires, logging).

  • Different ecosystems have varying capacities to respond to disturbances; resilience is the ability to absorb, adapt to, or recover from disturbances while maintaining ecosystem services, structure, and biodiversity.

  • Components of resilience include:

    • Resistance: the ability to withstand stress without significant change (e.g., mature forests resisting fire due to biodiversity and structure).

    • Recovery: the speed and extent to which an ecosystem returns to its pre-disturbance state.


Succession and its stages

  • Ecological succession is the transition from one biotic community to another following a disturbance.

  • Pioneer species colonize first and facilitate subsequent stages (facilitation).

  • Succession does not proceed indefinitely; it can be punctuated or redirected by disturbances.

  • Climax ecosystem: final, relatively stable stage of succession, though it can change if new disturbances or species alter conditions.

  • Adjacent ecosystems in the same environment can be at different successional stages.


Primary and secondary succession

  • Primary succession: occurs in areas lacking soil and vegetation (e.g., retreating glaciers); begins with bare rock and proceeds to soil formation and vegetation.

  • Secondary succession: occurs after a disturbance clears an area but soil remains; surrounding plants/animals reinvade and re-establish the community (e.g., after fire or floods).

  • Typical sequence (example) includes pioneer grasses, tall grasses/herbaceous plants, pines, and eventually hardwood forests (hardwoods) leading to a climax forest over decades.


Aquatic succession

  • Succession also occurs in lakes and ponds:

    • Soil and sediments erode into the water body, gradually filling it.

    • Terrestrial species move into the lake; aquatic species retreat, and over time the lake may disappear.


Fire, disturbance, and resilience in succession

  • Fire is a major disturbance shaping many ecosystems.

  • Species exhibit varying fire tolerances:

    • Grasses and pines tolerate fire; broad-leaved trees are more susceptible.

  • Fire recycles nutrients from dead organic matter and in some ecosystems is essential for germination and maintenance (e.g., fire-climax ecosystems such as certain grasslands and pine forests).

  • Resilience mechanisms include nutrient renewal, regrowth from seeds and roots, and recolonization; but resilience has limits—severe disturbances can lead to a degraded ecosystem with altered functioning.


Ecosystem capital and services

  • Ecosystems provide valuable services to humans and other species, including flood control, soil maintenance, CO₂ storage, and nutrient cycling.

  • These goods and services are not always captured by market prices; non-market values are substantial and essential for well-being.

  • An ecosystem’s services contribute to human welfare; estimates suggest a broad range of services have a multitrillion-dollar impact.

  • A notable figure cited: 17 major ecosystem goods and services contribute about $44 trillion to human welfare each year, which is over half of global GDP.

  • The concept of ecosystem capital emphasizes the economic value of the relationships between ecosystem changes and human welfare.

  • Example illustrating ecosystem service valuation and losses:

    • Converting 1 hectare of forest to an oil palm plantation can yield $1,000 to $2,000 in annual revenue but incur ecosystem service losses of $5,000 to $10,000 per hectare per year (losses include carbon storage, biodiversity, water regulation, etc.).

    • This demonstrates that the gains from exploitation often do not outweigh the losses in ecosystem services.


Ecosystem restoration and sustainable management

  • Ecosystem restoration is possible and may require intensive effort from restoration scientists.

  • There are growing pressures on Earth to provide goods and services (e.g., land for agriculture, irrigation, deforestation for agriculture; land and energy for infrastructure).

  • Alternatives can be pursued when:

    • Society recognizes the essential role of ecosystems.

    • Ecosystem sustainability is promoted.

    • Alternatives are economically viable.


Managing ecosystems and institutions

  • Understanding ecosystem function, disturbance responses, and the goods/services provided is essential for management.

  • In the United States, agencies that engage in ecosystem management include:

    • U.S. Forest Service

    • Department of Wildlife and Fisheries

    • National Park Service

    • Environmental Protection Agency (EPA)

    • NOAA (National Oceanic and Atmospheric Administration)


Practical and ethical implications

  • Valuing ecosystem services helps justify conservation and restoration investments beyond market prices.

  • Trade-offs between economic development and ecosystem health must be evaluated, including potential long-term losses from ecosystem degradation.

  • Restoration aims to recover ecosystem structure and function, but it may not fully restore original conditions or biodiversity, and may require ongoing management.

  • Policy and planning should emphasize precaution, resilience, and sustainability to maintain ecosystem services for future generations.


Quick reference formulas and numbers (key points)

  • Photosynthesis equation (summary):
    6\,CO{2} + 6\,H{2}O + \text{light energy} \rightarrow C{6}H{12}O{6} + 6\,O{2}

  • Energy transfer efficiency between trophic levels (typical):
    \text{Biomass}{n+1} \approx 0.1 \times \text{Biomass}n
    (about a 90% decrease per trophic step)

  • Primary production efficiency (solar energy capture):
    \eta \approx 2\%

  • Global primary production scale (terrestrial estimate):
    \text{Total OM produced per year} \approx 120\ \text{gigatons (Gt) of OM/year}

  • Fate of energy (typical ranges):

    • Energy used for metabolism/maintenance: 60\%\text{–}90\%

    • Energy converted to tissue: 10\%\text{–}40\%

  • Waste and excretion contribute to nutrient cycling (CO₂, N, P, H₂O).

  • Economic scale (ecosystem services):

    • 17 major ecosystem services: approx. 44\times 10^{12} USD/year (about half of global GDP).

    • Replacement or conversion costs can exceed gains: example of forest-to-palm conversion shows net ecosystem service losses of 5{,}000\$\text{–}10{,}000\$\text{ per hectare per year} alongside lower immediate revenue ($$1{,}000\$\text{–}2{,}000\$ per hectare/year).