Multi-jurisdictional cooperation is a key element of wildlife protection and illegal wildlife trafficking. Strategies to reduce the pressurse of illegal and unsustainable trade on biodiversity - and enhance the benefits to wildlife conservation and human well-being that derive from trade at sustainable levels - require cooperation between conservations, law enforcement, customs, and private industry.

Wildlife crime is not purely a conservation issue, as its adverse impacts also threaten sustainable development, good governance, rule of law, and national security.

The aim of this building block is to identify the risks and vulnerabilities of money laundering and how it relates to wildlife crimes. Additionally, this building block endeavours to provide guidance and recommendations to law enforcement and related personnel to enhance the financial aspect of wildlife crime investigations.

Fraudulent paperwork can transform wildlife contraband into seemingly legitimate merchandise, enabling it to be openly traded and evade interdiction. There are many schemes that criminals use to create fraudulent wildlife paperwork, including false declarations of captive breeding, purchasing paperwork from corrupt officials, forging paperwork, re-using or altering old permits, etc. Forensic accounting is therefore an important building block

The stores of traditional knowledge in upland Cambodia are rich and greatly varied, and include knowledge on conserving nature, health protection, farming systems, and plant and animal species uses and management.

These stores of knowledge reflect the varied geographic areas indigenous peoples and minorities live in, as well as the groups’ respective needs. All societies have utilized the natural environment for sustenance and succour, and the use of plants for medicinal treatment is therefore especially well developed across the globe.

As such, research institutions, private pharmaceutical companies and NGOs have in recent years recognized the importance of conserving this knowledge, but also using it to create benefits, which have not always been equitably shared. The absence of a system for the protection of traditional knowledge can easily result in the further erosion of this valuable knowledge and a permanent loss to local and indigenous communities, the country and the global community at large.

Failure to bring fair and equitable sharing of benefits from the utilization the traditional knowledge and genetic resources - especially for indigenous peoples and local communities - is a key constraint for the effective conservation of biodiversity.

The design and implementation of the flood canal take into consideration different levels of water.

During periods of relatively low water levels (below the 5-yr level), the canal resembles a natural stream. A small flow of water runs through gravel and stones, passes over a weir, scatters in shallow areas, and eventually disappears among wetland plants. This scenic stream continues even on non-rainy days through the use of stored rainwater.

At the 30-year level, the canal serves as a boundary for different types of plants. Above this level, groups of trees and shrubs are planted, while below it, various species of Miscanthus are cultivated. These plants are well-suited to fluctuating water levels and protect against the force of large flood flows.

At the 50-year level, all pathways in the park are elevated above the flood level, ensuring that they remain accessible and cannot be submerged. Along the canal, various amenities are strategically placed to cater to the well-being, comfort, and enjoyment of the citizens. This includes gym facilities, a basketball court, a playground, and shaded seating areas.

Overall, the flood canal area is designed to provide a pleasurable experience for visitors, offering a sense of tranquility, recreational opportunities, and a connection with nature.

Wetlands (willow ponds) have is a unique and poetic riverside landscape in the semi-arid Loess Plateau. Recognizing the importance of preserving this distinctive habitat and native flora and fauna along the Qingshui River, the willow ponds were kept with water supported from the Qingshui River.

This conservation effort becomes increasingly important as the existing landscape along the River continues to disappear. By using the existing drainage route as the main line for the flood canal, the impact of development is minimized. This approach reduces the need for soil displacement and lowers the risk of soil collapse, striking a balance between flood control and environmental preservation.

Furthermore, the design incorporates a soft grass area in the side slope of the canal as much as possible. This choice aims to enhance the aesthetic appeal and livability of the canal area. Additionally, the bottom of the canal is kept permeable,  to improve the overall quality of the canal as a living space.

By carefully considering these design elements, the project seeks to create a harmonious and sustainable flood canal system that not only manages water flow but also preserves and enhances the unique landscape of the semi-arid Loess Plateau.

The design approach for the flood canal seems well-thought-out. Diverting water through a weir into two pathways based on rainfall intensity allows for adaptability during different flood conditions.

Below the 5-year flooding level, the water is directed along a branch line to a wetland area, serving as a means for natural purification and infiltration of the water.

For higher flood levels, the canal incorporates an overtopping mechanism at the diversion weir, diverting excess water to the river via a flood channel, for up to a 50-year return period.

Consideration of various flood levels (5-year, 30-year, and 50-year) is important for erosion control measures. Different design strategies, such as impervious concretion base for the 5-year flood, retaining walls along the slope for the 30-year flood, and pervious surface measures above that level due to low erosion risk, help meet the requirements of each flood level and velocity.

Overall, the design of the flood canal appears to account for ecological concerns, varying flood conditions, and the management of sedimentation and erosion.

Before 1990, the area around Bau Sau was under severe pressures from local communities in Dak Lua Commune. Local people often entered the park for harvesting timber, fishing, and hunting animals. Conflicts between locals and forest rangers occurred frequently and seriously (with death, and a ranger station was burnt in 1990).

After establishment, the park managers focused on law enforcement. Number of donor projects in this period helped improving local livelihoods through productive and effective farming, e.g. irrigation, increasing rice crops cultivation from twice to three times/year, high yielding maize. With consensus from local people, households living in the core zone were supported to relocate to the buffer zones. Forest protection contracts were signed with local households, forest protection teams were established in villages around the park. Illegal activities were sharply reduced. Relationship with local communities has been improved, pressures on natural resources has reduced, and the habitat quality has been enhanced.

Along with proactive habitat restoration measures, wild fauna populations recovered rapidly. In addition to the Siamese Crocodile population that was re-established in Bau Sau area, other populations of animals of conservation concerns such as Gaur, and Green Peafowl etc. are well maintained.

In 1998, site managers and scientists discussed the possibility of reintroducing a crocodile population at Bau Sau. This was because the lake was situated in the historical occupation range of the species, and at that time, the habitat quality had been improved and ready for a reintroduction program. Feasibility studies were carried out. The park also held discussions among experts, managers, and authorities at all levels to gain consensus on the program.

In 2000, with the support from international experts, purebred Siamese Crocodiles, which are believed to have provenance from Cat Tien area, were selected from a farm in Ho Chi Minh City, to training for restoring their natural behaviours. From 2001 to 2005, a total of 60 adults were released into Bau Sau. In September 2005, the first baby crocodiles were recorded.

Recent monitoring shows that the number of individuals is increasing, the distribution area is also expanding with records in some neighbouring lakes. As of 2019, monitoring data has recorded at least 286 individuals (including 228 juveniles). Up to now, it can be confirmed that freshwater crocodile populations have been successfully re-established in Cat Tien National Park. The number and structure of the recorded population ensures that this is a healthy and viable population.

Producers must also have to commit not to kill predators and to be part of a more environmentally friendly production. A final key aspect is that the conservationist using this technique will have to invest a considerable amount of time between training the dog, selecting puppy candidates, constant monitoring and much more. If the social factors mentioned before are not taken into account and these commitments are not met, the success of the project would not be possible.