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Table 4.8 Ap<strong>pro</strong>ved re<strong>for</strong>estation, watershed-management, health and/or <strong>environmental</strong>enhancement<br />

<strong>pro</strong>jects under ER No. 1-94, by type of <strong>pro</strong>ject, January 1995 to June 2002<br />

Type of <strong>pro</strong>ject<br />

Year Nursery/<br />

reaf<strong>for</strong>estation/agro<strong>for</strong>estry<br />

Erosion/<br />

structural<br />

measures a<br />

Health<br />

ctr/med<br />

facility/<br />

equipment<br />

Water-<br />

supply<br />

system b<br />

80<br />

Com-<br />

munal<br />

toilets<br />

Solid-<br />

waste<br />

manage-<br />

ment<br />

Tra<strong>in</strong><br />

-<strong>in</strong>g<br />

1995 1 - 3 8 - - - 1<br />

1996 1 1 10 3 - 1 - -<br />

1997 3 - - 8 - 3 - 1<br />

1998 2 5 18 27 1 - - 1<br />

1999 3 4 31 28 2 8 - 6<br />

2000 10 10 29 36 3 10 2 8<br />

2001 4 1 11 5 1 2 - 2<br />

2002 2 1 8 11 1 2 - 4<br />

Unclas-<br />

sified c<br />

Total 26 22 110 126 8 26 2 23<br />

% of<br />

Total 8% 6% 32% 37% 2% 8% 1% 7%<br />

a/ Includes flood control.<br />

b/ Includes irrigation <strong>pro</strong>jects.<br />

c/ ncludes fire trucks, CRM <strong>pro</strong>jects, heavy equipment purchase, patrol boat purchase, slaughterhouse construction.<br />

Source: Energy Industry Adm<strong>in</strong>istration Bureau, Department of Energy, 2002.<br />

Moreover, <strong>the</strong>se <strong>environmental</strong>-enhancement <strong>pro</strong>jects are concentrated only <strong>in</strong> a few areas.<br />

For <strong>in</strong>stance, five watershed rehabilitation <strong>pro</strong>jects, and six erosion-control ones, were<br />

established <strong>in</strong> Pagbilao, Quezon, all with<strong>in</strong> <strong>the</strong> same year (2000). Three watershed<br />

rehabilitation <strong>pro</strong>jects <strong>in</strong> 2001, and two erosion control <strong>pro</strong>jects <strong>in</strong> 2001 and 2002, were all<br />

likewise implemented <strong>in</strong> <strong>the</strong> same municipality. It just so happened that <strong>the</strong> concerned LGU<br />

had a <strong>pro</strong>clivity towards <strong>environmental</strong> <strong>in</strong>vestments, relative to <strong>the</strong> o<strong>the</strong>r host communities.<br />

Hence, <strong>the</strong> choice of such <strong>pro</strong>jects becomes even more isolated on a per host community<br />

basis.<br />

Noticeable is <strong>the</strong> column of unclassified <strong>pro</strong>jects, whereby <strong>the</strong>re were certa<strong>in</strong> <strong>pro</strong>jects funded<br />

that did not fall under any of <strong>the</strong> allowed categories. In fact, many of <strong>the</strong>se <strong>pro</strong>jects are<br />

actually allowed under <strong>the</strong> DLF, such as slaughterhouses and irrigation <strong>pro</strong>jects (see Table<br />

4.8). Flood-control measures were classified with erosion-control measures, albeit such<br />

<strong>pro</strong>jects are supposed to be funded under <strong>the</strong> DLF. There may have been honest mistakes <strong>in</strong><br />

sourc<strong>in</strong>g funds <strong>for</strong> such <strong>pro</strong>ject <strong>pro</strong>posals. But a more plausible explanation is <strong>the</strong> fact <strong>the</strong><br />

RWMHEEF funds are easier to ga<strong>in</strong> access to, due to more flexibility <strong>in</strong> <strong>the</strong> amounts that<br />

LGUs can request. For those unclassified <strong>pro</strong>jects that could not be <strong>in</strong>cluded <strong>in</strong> ei<strong>the</strong>r fund,<br />

<strong>the</strong>se could have been <strong>pro</strong>jects that were accompanied by strong political pressure, or had a<br />

sense of urgency as far as endorsement of <strong>the</strong> energy <strong>pro</strong>ject was concerned.<br />

Accord<strong>in</strong>g to <strong>the</strong> data ga<strong>the</strong>red from <strong>the</strong> DOE, <strong>the</strong>re does not seem to be a specific target<strong>in</strong>g<br />

of beneficiaries by type. Each <strong>pro</strong>ject <strong>pro</strong>posal conta<strong>in</strong>s a summary of basic data, <strong>in</strong>clud<strong>in</strong>g<br />

<strong>the</strong> number of beneficiaries. The <strong>pro</strong>posals simply <strong>in</strong>dicate <strong>the</strong> total population of <strong>the</strong> area as<br />

<strong>the</strong> target beneficiaries. Hence, <strong>the</strong>re is no relevant analysis that can be made on this aspect.<br />

4.2.7 Socio-economic impact analysis<br />

In test<strong>in</strong>g <strong>the</strong> methodology <strong>for</strong> this case study, data ga<strong>the</strong>r<strong>in</strong>g relied ma<strong>in</strong>ly on secondary<br />

sources – <strong>the</strong> DOE and <strong>the</strong> NPC. An attempt was made to visit some of <strong>the</strong> watershed<br />

rehabilitation and re<strong>for</strong>estation <strong>pro</strong>jects ap<strong>pro</strong>ved dur<strong>in</strong>g <strong>the</strong> past three years. Un<strong>for</strong>tunately,

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