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FINAL VERSION FOR APPROVAL - Sdn Bhd - WWF Malaysia

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Gunung Stong State Park Preliminary Management Plan<br />

BOD mg/l 0.66 0.54 0.68 0.69 0.50 1.42 0.90 0.66 0.84 0.88 0.40 0.92<br />

COD mg/l 1 1 1 1 1 1 1 5 1 6 1 1<br />

NH3N mg/l 0.02 0.02 0.05 0.02 0.03 0.01 0.04 0.05 0.03 0.03 0.03 0.02<br />

NO 3N mg/l 3.6 5.4 3.1 4.2 1.7 5.0 3.2 2.5 1.4 1.4 4.0 5.0<br />

NO 2N mg/l 0.00<br />

2<br />

0.00<br />

3<br />

0.00<br />

6<br />

0.01<br />

1<br />

0.01<br />

1<br />

PO 4 mg/l 0.46 0.07 0.67 0.44 0.20 0.23 0.58 1.19 0.42 0.60 0.23 0.29<br />

SO 4 mg/l 1 1 2 1 2 2 2 1 5 2 1 1<br />

Cu mg/l 0.00 0.01 0.01 0.01 0.54 0.08 0.00 0.01 0.09 0.09 0.01 0.05<br />

E. coli MPN/<br />

100ml<br />

0.00<br />

1<br />

0.00<br />

4<br />

0.00<br />

4<br />

0.00<br />

5<br />

0.00<br />

7<br />

0.00<br />

6<br />

365 148 365 866 488 980 1,733 2,419 260 980 64 411<br />

TSS Mg/l 1.4 1.6 6.2 1.6 1.6 2.7 7.0 4.3 1.5 0.5 11 0.5<br />

WQI 100 100 100 100 100 100 100 100 100 100 100 100<br />

Class I I I I I I I I I I I I<br />

Source: Mohd Kamil et al. (2005)<br />

All the waters sampled at the points S1 to S12 exhibited INWQS Class I characteristics,<br />

indicative of excellent water quality, especially in relation to its neutral pH, high dissolved<br />

oxygen (DO), low turbidity, low total suspended solids (TSS), low carbon oxygen demand<br />

(COD) and biological oxygen demand (BOD), and low levels of nitrates, phosphates,<br />

sulphates, and copper. Nevertheless, an area of concern is the level of E. coli at certain<br />

sampling stations, indicative of fecal contamination, especially at S8 (2,419/100ml), S7<br />

(1,733/100ml), S10 (980/100ml), S6 (980/100ml), and S4 (866/100ml). Except for S10, all<br />

the sites are at or near human habitations, especially in the resort area, dwelling units, and the<br />

Baha Camp.<br />

Regular monitoring is a must, in order to determine the water (sewage) quality patterns and<br />

trends, in view of the fact that the Sg. Jeri is a source of potable water for the Jelawang<br />

community. Discharge of raw sewage may be the limiting factor in additional infrastructural<br />

construction for accommodation at the resort or at Baha Camp, unless a proper sewage<br />

treatment facility is made available for mitigating the additional sewage load into the Sg. Jeri.<br />

2.7 Land Use<br />

The study area is heavily forested, with some 80% under Permanent Forest Reserves,<br />

followed by agricultural land under rubber, fruits and oil palm, and settlements (refer to<br />

Appendix 4 for the land use map). Federal and state agricultural agencies (FELCRA,<br />

KESEDAR, RISDA, PKENK) play a major role in conversion of forest to agricultural<br />

smallholdings, as a land-reform programme for the poor and landless.<br />

Land use for the Kuala Krai district (as described in Table 2.4 below) could be representative<br />

of the area surrounding GSSP.<br />

Table 2.4: Land Use of the District of Kuala Krai<br />

No Land Use Area (ha) Percentage<br />

(%)<br />

1. Forest Reserves 112,779.6 47.8<br />

2. Reserves/Roads/Others 71,670.0 30.4<br />

3. Rubber 25,959.0 11.0<br />

4. Orchards and others 18,169.2 7.5<br />

0.00<br />

7<br />

26

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