A government environmental agency in a province of Southeast Asia has been monitoring the mangrove forests along its southern coastline. The province contai...

Assessment: Environmental Management 0680 | Paper 2 Mock 01 | Environmental Management in Context Subject: Environmental Management - 0680

Question 1 Report

A government environmental agency in a province of Southeast Asia has been monitoring the mangrove forests along its southern coastline. The province contains one of the largest remaining coastal mangrove ecosystems in the region, covering an area of tidal mudflats and estuaries where several rivers flow into the sea. Mangrove trees are adapted to grow in salty, waterlogged soil in the intertidal zone. Their dense root systems create a complex underwater habitat that supports a wide variety of fish, crustaceans and other organisms.

Fig. 1 shows a simplified food web for the mangrove ecosystem.

diagram

Since the early 1980s, the aquaculture industry has expanded rapidly across the coastal zone. Large areas of mangrove forest have been cleared and converted into commercial shrimp ponds. Shrimp farming generates significant export income for the province, but environmental organisations have raised concerns about the long-term consequences of mangrove removal.

Table 1 shows data collected by scientists at monitoring stations along the coast between 1980 and 2020.

Table 1: Mangrove ecosystem monitoring data, 1980 to 2020
YearMangrove area (km2)Number of fish speciesNumber of bird speciesShrimp farm area (km2)
1980850124875
19907201187945
20005409862130
20104107648210
20203807143245

Fishing communities along the coast have reported declining fish catches each year. Research conducted by the national university found that mangrove root systems provide critical ecosystem services including nursery habitat for juvenile fish, nutrient cycling through decomposing leaf litter, sediment trapping that maintains water clarity for offshore seagrass beds, and natural coastal defence against storms and flooding. During major storm events in 2004 and 2013, villages protected by intact mangrove forest suffered significantly less damage than communities where mangroves had been removed. Coastal engineers estimated that one kilometre of healthy mangrove forest provides wave protection equivalent to an artificial sea wall costing approximately US $300 000 to construct.

The government is now considering policy options for the remaining mangrove areas. Proposals include establishing protected zones, promoting integrated mangrove-aquaculture systems, funding community conservation programmes, and investing in replanting degraded coastline.

(a)(i) State the meaning of the term 'ecosystem'. [2]

(a)(ii) Using Fig. 1, identify two producers in the mangrove food web. [2]

(b)(i) Using Fig. 1, construct one food chain containing four organisms from the mangrove food web. [2]

(b)(ii) State the trophic level of each organism in your food chain from (b)(i). [2]

(c)(i) Use the data in Table 1 to describe the changes in mangrove area between 1980 and 2020. [3]

(c)(ii) Describe the changes in species diversity shown in Table 1 over the same period. [3]

(d) Explain why the decrease in mangrove area is likely to reduce fish populations in the coastal waters. [5]

(e)(i) Describe how mangroves protect coastal areas from wave damage and erosion. [3]

(e)(ii) Explain why the loss of mangroves increases the risk of damage from storms and flooding. [3]

(f) Using Table 1, explain the conflict between shrimp aquaculture expansion and mangrove conservation. [4]

(g) Suggest how the government could balance economic development with conservation of the mangrove ecosystem. [4]

(h) Evaluate strategies for the sustainable management of mangrove ecosystems. Suggest which strategy would be most effective and justify your choice. [7]

Answer Details

(a)(i) An ecosystem is a community of living organisms (the biotic component) [1] interacting with their non-living (abiotic) environment - such as water, temperature, light and soil - within a defined area [1]. The mangrove ecosystem described here is a good example: mangrove trees, fish, crabs and birds (biotic) interact with salty water, tidal mudflats and nutrient cycles (abiotic) in the intertidal zone.

(a)(ii) From Fig. 1, two producers in the mangrove food web are any two of: mangrove leaves, seagrass, phytoplankton, or algae [1 each, max 2]. Producers are organisms that make their own food through photosynthesis. They form the base of the food web, converting sunlight energy into chemical energy that is then passed to consumers at higher trophic levels.

(b)(i) A valid food chain containing four organisms from the mangrove food web is:

Seagrass \(\rightarrow\) Prawns \(\rightarrow\) Large fish \(\rightarrow\) Crocodile [2]

This chain must follow the arrows shown in Fig. 1. Each arrow represents energy transfer from prey to predator. Other valid chains include: Algae \(\rightarrow\) Small fish \(\rightarrow\) Large fish \(\rightarrow\) Crocodile, or Mangrove leaves \(\rightarrow\) Crabs \(\rightarrow\) Heron \(\rightarrow\) (only three levels, so not valid for four organisms). [1 mark if only three organisms are correctly linked.]

(b)(ii) Using the example chain above:

OrganismTrophic level
SeagrassProducer (trophic level 1)
PrawnsPrimary consumer (trophic level 2)
Large fishSecondary consumer (trophic level 3)
CrocodileTertiary consumer (trophic level 4)

[1] for correctly identifying the producer. [1] for correctly identifying at least two consumer trophic levels. Each trophic level represents a feeding stage. Energy is transferred from one level to the next, but approximately 90% is lost at each stage (mainly as heat through respiration), which is why food chains rarely exceed four or five levels.

(c)(i) Between 1980 and 2020, the mangrove area decreased from 850 km2 to 380 km2 [1]. This is a total decrease of 470 km2, or approximately 55% of the original area [1]:

\[\text{Percentage decrease} = \frac{850 - 380}{850} \times 100 = 55.3\%\]

The rate of loss was not constant. The greatest loss occurred between 1990 and 2000, when 180 km2 was cleared (720 to 540). After 2010, the rate of loss slowed considerably, with only 30 km2 lost in the final decade (410 to 380) [1]. This slowing may reflect the fact that the remaining mangrove is harder to access, or that awareness of mangrove value has grown.

(c)(ii) Fish species declined from 124 to 71, a loss of 53 species or approximately 43% [1]. Bird species declined from 87 to 43, a loss of 44 species or approximately 51% [1]. Both measures of biodiversity declined as mangrove area decreased, showing a strong correlation between habitat loss and species decline [1]. The decline in bird species was proportionally greater than fish species. This is because many bird species (such as herons) depend on the mangrove canopy for nesting and on the fish and invertebrates within the mangrove for food - losing the mangrove removes both their habitat and their food supply simultaneously.

(d) The decrease in mangrove area reduces fish populations through several interconnected mechanisms:

  1. Loss of nursery habitat: Mangrove root systems create sheltered areas where juvenile fish can grow in safety from larger predators. Fewer mangroves means fewer breeding and nursery grounds, so fewer young fish survive to adulthood [1].
  2. Reduced food supply: Mangrove roots support communities of crabs, prawns and invertebrates that fish feed on. As shown in Fig. 1, crabs and prawns are primary consumers that feed large fish - removing the mangrove habitat reduces these prey populations [1].
  3. Disrupted nutrient cycling: Decomposing mangrove leaves release nutrients and detritus that form the base of the food web. Leaf litter provides energy for bacteria and small organisms, which are consumed by larger animals. Without this input, the entire food web loses its energy foundation [1].
  4. Reduced water quality: Mangrove roots filter sediment and pollutants from the water. Without this filtration, increased turbidity blocks sunlight from reaching seagrass beds, reducing photosynthesis by another producer in the food web and further degrading the habitat [1].
  5. Reduced energy at higher trophic levels: Loss of producers (mangrove leaves, seagrass) at the base of the food web reduces the total energy available to support all higher trophic levels. Since energy transfer between levels is only about 10% efficient, any reduction at the base has a magnified effect on fish populations higher up [1].

(e)(i) Mangroves protect coastal areas through three main mechanisms:

  1. The dense root network acts as a physical barrier that absorbs and dissipates wave energy before it reaches the shore. The complex tangle of aerial roots forces water to slow down and spread out [1].
  2. Mangrove roots stabilise coastal sediment and prevent erosion by binding soil particles together. Without roots anchoring the sediment, waves would wash it away, causing the coastline to retreat [1].
  3. Mangroves reduce the height and force of storm surges by creating friction that slows the advancing water, protecting the land behind them from flooding [1].

(e)(ii) Without mangroves, the coast becomes significantly more vulnerable:

  1. Wave energy reaches the coast undiminished, causing rapid erosion of beaches, banks and land [1].
  2. Coastal communities lose their natural barrier against storms and flooding. The passage notes that during storm events in 2004 and 2013, villages with intact mangroves suffered significantly less damage [1].
  3. Replacing natural mangrove protection with artificial sea walls is extremely expensive - approximately US $300,000 per kilometre of coastline. This represents a loss of valuable ecosystem services that were previously provided for free by the mangroves [1].

(f) Table 1 reveals a clear conflict between economic development and environmental conservation:

  1. Shrimp farm area increased from 5 km2 to 245 km2 while mangrove area decreased from 850 km2 to 380 km2, showing that mangrove forest was cleared to create shrimp ponds [1].
  2. Shrimp farming generates significant export income, providing economic benefits for the province through employment and revenue [1].
  3. However, mangrove removal caused fish species to decline from 124 to 71, threatening traditional fishing livelihoods that communities have depended on for generations [1].
  4. Mangroves provide free ecosystem services including coastal protection (equivalent to $300,000/km in sea wall construction), nursery habitat for commercial fish, water filtration and carbon storage. These services have real economic value but are lost permanently when mangroves are cleared for aquaculture [1].

(g) The government could balance economic development with conservation through several approaches:

  1. Establish protected zones where no further mangrove clearing is permitted, safeguarding the remaining 380 km2 of habitat and its ecosystem services [1].
  2. Promote integrated mangrove-aquaculture systems where shrimp ponds coexist alongside standing mangrove forest. In these systems, mangroves filter water for the ponds while the ponds benefit from the natural nutrient cycling [1].
  3. Fund community-based conservation programmes that give local people economic incentives - such as payments for ecosystem services or employment as mangrove wardens - to protect rather than clear mangroves [1].
  4. Invest in replanting degraded areas of coastline with mangrove seedlings. Although restored mangroves take years to mature, replanting begins the process of recovering lost ecosystem services [1].

(h) An evaluation of strategies for sustainable mangrove management:

1. Protected areas: Legally preventing clearance ensures that remaining mangroves are preserved and continue to provide ecosystem services [1]. However, enforcement can be difficult and expensive, especially in remote coastal areas where resources are limited and illegal clearance may continue [1].

2. Replanting programmes: Replanting restores mangrove cover in degraded areas and can rebuild ecosystem services over time [1]. However, restored mangroves take decades to reach maturity. Young plantations may not support the same level of biodiversity as original old-growth forest, and some replanting schemes have had low survival rates [1].

3. Sustainable aquaculture: Developing shrimp farming methods that do not require mangrove clearance - such as inland ponds or integrated mangrove-aquaculture systems - addresses the root economic driver of destruction [1]. This allows aquaculture to continue generating income while preserving the mangroves [1].

Most effective strategy: Sustainable aquaculture combined with community management is likely most effective because it addresses the economic pressure that drives clearance in the first place. Simply prohibiting development may be ignored if people have no alternative livelihood. When local communities have an economic stake in preserving the mangroves (through sustainable aquaculture, ecotourism, or payments for ecosystem services), they become active participants in conservation rather than being forced to choose between their livelihoods and the environment [1]. [Max 7 marks]

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